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California Saltwater Sport Fishing Regulations
2017–2018 CALIFORNIA SALTWATER SPORT FISHING REGULATIONS For Ocean Sport Fishing in California Effective March 1, 2017 through February 28, 2018 13 2017–2018 CALIFORNIA SALTWATER SPORT FISHING REGULATIONS Groundfish Regulation Tables Contents What’s New for 2017? ............................................................. 4 24 License Information ................................................................ 5 Sport Fishing License Fees ..................................................... 8 Keeping Up With In-Season Groundfish Regulation Changes .... 11 Map of Groundfish Management Areas ...................................12 Summaries of Recreational Groundfish Regulations ..................13 General Provisions and Definitions ......................................... 20 General Ocean Fishing Regulations ��������������������������������������� 24 Fin Fish — General ................................................................ 24 General Ocean Fishing Fin Fish — Minimum Size Limits, Bag and Possession Limits, and Seasons ......................................................... 24 Fin Fish—Gear Restrictions ................................................... 33 Invertebrates ........................................................................ 34 34 Mollusks ............................................................................34 Crustaceans .......................................................................36 Non-commercial Use of Marine Plants .................................... 38 Marine Protected Areas and Other -
CHECKLIST and BIOGEOGRAPHY of FISHES from GUADALUPE ISLAND, WESTERN MEXICO Héctor Reyes-Bonilla, Arturo Ayala-Bocos, Luis E
ReyeS-BONIllA eT Al: CheCklIST AND BIOgeOgRAphy Of fISheS fROm gUADAlUpe ISlAND CalCOfI Rep., Vol. 51, 2010 CHECKLIST AND BIOGEOGRAPHY OF FISHES FROM GUADALUPE ISLAND, WESTERN MEXICO Héctor REyES-BONILLA, Arturo AyALA-BOCOS, LUIS E. Calderon-AGUILERA SAúL GONzáLEz-Romero, ISRAEL SáNCHEz-ALCántara Centro de Investigación Científica y de Educación Superior de Ensenada AND MARIANA Walther MENDOzA Carretera Tijuana - Ensenada # 3918, zona Playitas, C.P. 22860 Universidad Autónoma de Baja California Sur Ensenada, B.C., México Departamento de Biología Marina Tel: +52 646 1750500, ext. 25257; Fax: +52 646 Apartado postal 19-B, CP 23080 [email protected] La Paz, B.C.S., México. Tel: (612) 123-8800, ext. 4160; Fax: (612) 123-8819 NADIA C. Olivares-BAñUELOS [email protected] Reserva de la Biosfera Isla Guadalupe Comisión Nacional de áreas Naturales Protegidas yULIANA R. BEDOLLA-GUzMáN AND Avenida del Puerto 375, local 30 Arturo RAMíREz-VALDEz Fraccionamiento Playas de Ensenada, C.P. 22880 Universidad Autónoma de Baja California Ensenada, B.C., México Facultad de Ciencias Marinas, Instituto de Investigaciones Oceanológicas Universidad Autónoma de Baja California, Carr. Tijuana-Ensenada km. 107, Apartado postal 453, C.P. 22890 Ensenada, B.C., México ABSTRACT recognized the biological and ecological significance of Guadalupe Island, off Baja California, México, is Guadalupe Island, and declared it a Biosphere Reserve an important fishing area which also harbors high (SEMARNAT 2005). marine biodiversity. Based on field data, literature Guadalupe Island is isolated, far away from the main- reviews, and scientific collection records, we pres- land and has limited logistic facilities to conduct scien- ent a comprehensive checklist of the local fish fauna, tific studies. -
Saccular Otolith Mass Asymmetry in Adult Flatfishes 2581
Journal of Fish Biology (2008) 72, 2579–2594 doi:10.1111/j.1095-8649.2008.01869.x, available online at http://www.blackwell-synergy.com Saccular otolith mass asymmetry in adult flatfishes D. V. LYCHAKOV*†,Y.T.REBANE‡, A. LOMBARTE§, M. DEMESTRE§ AND L. A. FUIMANk *Sechenov Institute of Evolutionary Physiology and Biochemistry of Russian Academy of Sciences, St Petersburg, Thorez pr., 44, 194223, Russia, ‡Ioffe Physical Technical Institute of Russian Academy of Sciences, Politekhnicheskaya 26, St Petersburg 194021, Russia, §Departament de Recursos Marins Renovables, Institut de Cie`ncies del Mar-CMIMA (CSIC), Passeig Marıtim´ 37-49, 08003 Barcelona, Catalonia, Spain and kDepartment of Marine Science, University of Texas at Austin, Marine Science Institute, 750 Channel View Drive, Port Aransas, TX 78373-1267, U.S.A. (Received 29 June 2007, Accepted 20 February 2008) A dimensionless measure of otolith mass asymmetry, w, was calculated as the difference between the masses of the right and left paired otoliths divided by average otolith mass. Saccular otolith mass asymmetry was studied in eight flatfish species (110 otolith pairs) and compared with data from a previously published study on roundfishes. As in the case of symmetrical fishes, the absolute value of w in flatfishes does not depend on fish length and otolith growth rate, although otolith mass and the absolute value of otolith mass difference are correlated with fish length. The values of w were between À0Á2 and þ0Á2in96Á4% of flatfishes studied. The mean Æ S.E. value of w in flatfishes was significantly larger than in standard bilaterally symmetrical marine fishes (‘roundfishes’), respectively 0Á070 Æ 0Á006 and 0Á040 Æ 0Á006. -
Appendix E: Fish Species List
Appendix F. Fish Species List Common Name Scientific Name American shad Alosa sapidissima arrow goby Clevelandia ios barred surfperch Amphistichus argenteus bat ray Myliobatis californica bay goby Lepidogobius lepidus bay pipefish Syngnathus leptorhynchus bearded goby Tridentiger barbatus big skate Raja binoculata black perch Embiotoca jacksoni black rockfish Sebastes melanops bonehead sculpin Artedius notospilotus brown rockfish Sebastes auriculatus brown smoothhound Mustelus henlei cabezon Scorpaenichthys marmoratus California halibut Paralichthys californicus California lizardfish Synodus lucioceps California tonguefish Symphurus atricauda chameleon goby Tridentiger trigonocephalus cheekspot goby Ilypnus gilberti chinook salmon Oncorhynchus tshawytscha curlfin sole Pleuronichthys decurrens diamond turbot Hypsopsetta guttulata dwarf perch Micrometrus minimus English sole Pleuronectes vetulus green sturgeon* Acipenser medirostris inland silverside Menidia beryllina jacksmelt Atherinopsis californiensis leopard shark Triakis semifasciata lingcod Ophiodon elongatus longfin smelt Spirinchus thaleichthys night smelt Spirinchus starksi northern anchovy Engraulis mordax Pacific herring Clupea pallasi Pacific lamprey Lampetra tridentata Pacific pompano Peprilus simillimus Pacific sanddab Citharichthys sordidus Pacific sardine Sardinops sagax Pacific staghorn sculpin Leptocottus armatus Pacific tomcod Microgadus proximus pile perch Rhacochilus vacca F-1 plainfin midshipman Porichthys notatus rainwater killifish Lucania parva river lamprey Lampetra -
<I>Aplysia Californica</I>
Temperature Eff ects on Growth, Maturation, and Lifes- pan of the California Sea Hare (Aplysia californica) DUSTIN STOMMES, BLA, LYNNE A. FIEBER, PHD,* CHRISTINA BENO, ROBERT GERDES, MS, and THOMAS R. CAPO, BS We conducted a hatchery growth study to describe the variability in growth rates, spawning, and mortality of Aplysia californica in regard to rearing temperature. Animals were housed at a standard hatchery density of fi ve animals per cage, at temperatures of 13, 15, 18, and 21°C. Animals reared at 13 or 15°C grew as much as four times as large, lived twice as long, matured later, and spawned longer than did animals reared at 18 or 21°C. At age 170 to 205 days the fastest growth rates occurred at 18 and 21°C, and the slowest at 13°C. As animals at 18 and 21°C reached sexual maturity at ages 190 to 197 days, or ∼60% through their lifespans, their growth rates slowed such that by age 260 days, the fastest growth rate was at 13°C, and the slowest was at 21°C. Animals reared at 13 and 15°C reached sexual maturity at 242 and 208 days, respectively, or at ∼40% of their life spans. Lifespan and maximum average animal weight were signifi cantly inversely correlated with temperature (P ≤ 0.0001). However, there were no signifi cant diff erences at any temperature in the age at which maximum animal weight was reached when this age was expressed as a percentage of the life span: animals reached their maximum weight at ∼80% of their life span. -
US Fish & Wildlife Service Seabird Conservation Plan—Pacific Region
U.S. Fish & Wildlife Service Seabird Conservation Plan Conservation Seabird Pacific Region U.S. Fish & Wildlife Service Seabird Conservation Plan—Pacific Region 120 0’0"E 140 0’0"E 160 0’0"E 180 0’0" 160 0’0"W 140 0’0"W 120 0’0"W 100 0’0"W RUSSIA CANADA 0’0"N 0’0"N 50 50 WA CHINA US Fish and Wildlife Service Pacific Region OR ID AN NV JAP CA H A 0’0"N I W 0’0"N 30 S A 30 N L I ort I Main Hawaiian Islands Commonwealth of the hwe A stern A (see inset below) Northern Mariana Islands Haw N aiian Isla D N nds S P a c i f i c Wake Atoll S ND ANA O c e a n LA RI IS Johnston Atoll MA Guam L I 0’0"N 0’0"N N 10 10 Kingman Reef E Palmyra Atoll I S 160 0’0"W 158 0’0"W 156 0’0"W L Howland Island Equator A M a i n H a w a i i a n I s l a n d s Baker Island Jarvis N P H O E N I X D IN D Island Kauai S 0’0"N ONE 0’0"N I S L A N D S 22 SI 22 A PAPUA NEW Niihau Oahu GUINEA Molokai Maui 0’0"S Lanai 0’0"S 10 AMERICAN P a c i f i c 10 Kahoolawe SAMOA O c e a n Hawaii 0’0"N 0’0"N 20 FIJI 20 AUSTRALIA 0 200 Miles 0 2,000 ES - OTS/FR Miles September 2003 160 0’0"W 158 0’0"W 156 0’0"W (800) 244-WILD http://www.fws.gov Information U.S. -
Fertilization Selection on Egg and Jelly-Coat Size in the Sand Dollar Dendraster Excentricus
Evolution, 55(12), 2001, pp. 2479±2483 FERTILIZATION SELECTION ON EGG AND JELLY-COAT SIZE IN THE SAND DOLLAR DENDRASTER EXCENTRICUS DON R. LEVITAN1,2 AND STACEY D. IRVINE2 1Department of Biological Science, Florida State University, Tallahassee, Florida 32306-1100 2Bam®eld Marine Station, Bam®eld, British Columbia VOR 1B0, Canada Abstract. Organisms with external fertilization are often sperm limited, and in echinoids, larger eggs have a higher probability of fertilization than smaller eggs. This difference is thought to be a result of the more frequent sperm- egg collisions experienced by larger targets. Here we report how two components of egg target size, the egg cell and jelly coat, contributed to fertilization success in a selection experiment. We used a cross-sectional analysis of correlated characters to estimate the selection gradients on egg and jelly-coat size in ®ve replicate male pairs of the sand dollar Dendraster excentricus. Results indicated that eggs with larger cells and jelly coats were preferentially fertilized under sperm limitation in the laboratory. The selection gradients were an average of 922% steeper for egg than for jelly- coat size. The standardized selection gradients for egg and jelly-coat size were similar. Our results suggest that fertilization selection can act on both egg-cell and jelly-coat size but that an increase in egg-cell volume is much more likely to increase fertilization success than an equal change in jelly-coat volume. The strengths of the selection gradients were inversely related to the correlation of egg traits across replicate egg clutches. This result suggests the importance of replication in studies of selection of correlated characters. -
And Red Sea Urchins
NEGATIVELY CORRELATED ABUNDANCE SUGGESTS COMPETITION BETWEEN RED ABALONE (Haliotis rufescens) AND RED SEA URCHINS (Mesocentrotus franciscanus) INSIDE AND OUTSIDE ESTABLISHED MPAs CLOSED TO COMMERCIAL SEA URCHIN HARVEST IN NORTHERN CALIFORNIA By Johnathan Centoni A Thesis Presented to The Faculty of Humboldt State University In Partial Fulfillment of the Requirements for the Degree Master of Science in Biology Committee Membership Dr. Sean Craig, Committee Chair Dr. Brian Tissot, Committee Member Dr. Paul Bourdeau, Committee Member Dr. Joe Tyburczy, Committee Member Dr. Erik Jules, Program Graduate Coordinator May 2018 ABSTRACT NEGATIVELY CORRELATED ABUNDANCE SUGGESTS COMPETITION BETWEEN RED ABALONE (Haliotis rufescens) AND RED SEA URCHINS (Mesocentrotus franciscanus) INSIDE AND OUTSIDE ESTABLISHED MPAs CLOSED TO COMMERCIAL SEA URCHIN HARVEST IN NORTHERN CALIFORNIA Johnathan Centoni Red abalone and sea urchins are both important herbivores that potentially compete with each other for resources like food and space along the California coast. Red abalone supported a socioeconomically important recreational fishery during this study (which was closed in 2018) and red sea urchins support an important commercial fishery. Both red sea urchins and red abalone feed on the same macroalgae (including Pterygophora californica, Laminaria setchellii, Stephanocystis osmundacea, Costaria costata, Alaria marginata, Nereocystis leutkeana), and a low abundance of this food source during the period of this project may have created a highly competitive environment for urchins and abalone. Evidence that suggests competition between red abalone and red sea urchins can be seen within data collected during the years of this study (2014-2016): a significantly higher red sea urchin density, concomitant with a significantly lower red abalone density, was observed within areas closed to commercial sea urchin harvest (in MPAs) compared to nearby reference areas open to sea urchin harvest. -
Developmental Effects of Predator Cues on Dendraster Excentricus Larvae
Running head: Developmental Effects of Predator Cues on Dendraster excentricus Larvae Developmental Effects of Predator Cues on Dendraster excentricus Larvae: The Effects of Pugettia producta Effluent and Crustacean Dominant Plankton Effluent Claudia Mateo University of Washington Friday Harbor Laboratories Developmental Effects of Predator Cues on Dendraster excentricus Larvae Mateo 1 Abstract Previous findings supporting increased cloning in Dendraster excentricus (D. excentricus) larvae as a response to predator cues, in particular fish slime. Such findings report a “visual predator hypothesis”, suggesting that the larvae clone in order to become smaller and thereby avoid visual predators and possibly even non-visual predators. The experiment reported here builds upon earlier findings by studying the exposure of D. excentricus larvae to a kelp crab effluent (using Pugettia producta) and a crustacean dominant plankton effluent. Individual larvae were exposed to one of three treatments: the kelp crab effluent, plankton effluent, or filtered sea water, for approximately 66 hours. After this period, number of clones, number of larval arms, and the rudiment stage of each larvae was determined. Linear modeling showed significant results when comparing the kelp crab treatment to the control for cloning (p=0.024) and rudiment stage (p= 0.032); they also displayed significant differences for larval arm stage when comparing both the kelp crab effluent treatment (p= <0.001) and plankton effluent treatment (p= <0.001) to the control. These findings may support the visual predator theory, depending on whether D. excentricus larvae are able to differentiate predator cues, and, if so, to what specificity. Developmental Effects of Predator Cues on Dendraster excentricus Larvae Mateo 2 Introduction Dendraster excentricus (D. -
California Yellowtail, White Seabass California
California yellowtail, White seabass Seriola lalandi, Atractoscion nobilis ©Monterey Bay Aquarium California Bottom gillnet, Drift gillnet, Hook and Line February 13, 2014 Kelsey James, Consulting researcher Disclaimer Seafood Watch® strives to ensure all our Seafood Reports and the recommendations contained therein are accurate and reflect the most up-to-date evidence available at time of publication. All our reports are peer- reviewed for accuracy and completeness by external scientists with expertise in ecology, fisheries science or aquaculture. Scientific review, however, does not constitute an endorsement of the Seafood Watch program or its recommendations on the part of the reviewing scientists. Seafood Watch is solely responsible for the conclusions reached in this report. We always welcome additional or updated data that can be used for the next revision. Seafood Watch and Seafood Reports are made possible through a grant from the David and Lucile Packard Foundation. 2 Final Seafood Recommendation Stock / Fishery Impacts on Impacts on Management Habitat and Overall the Stock other Spp. Ecosystem Recommendation White seabass Green (3.32) Red (1.82) Yellow (3.00) Green (3.87) Good Alternative California: Southern (2.894) Northeast Pacific - Gillnet, Drift White seabass Green (3.32) Red (1.82) Yellow (3.00) Yellow (3.12) Good Alternative California: Southern (2.743) Northeast Pacific - Gillnet, Bottom White seabass Green (3.32) Green (4.07) Yellow (3.00) Green (3.46) Best Choice (3.442) California: Central Northeast Pacific - Hook/line -
Terrestrial and Marine Biological Resource Information
APPENDIX C Terrestrial and Marine Biological Resource Information Appendix C1 Resource Agency Coordination Appendix C2 Marine Biological Resources Report APPENDIX C1 RESOURCE AGENCY COORDINATION 1 The ICF terrestrial biological team coordinated with relevant resource agencies to discuss 2 sensitive biological resources expected within the terrestrial biological study area (BSA). 3 A summary of agency communications and site visits is provided below. 4 California Department of Fish and Wildlife: On July 30, 2020, ICF held a conference 5 call with Greg O’Connell (Environmental Scientist) and Corianna Flannery (Environmental 6 Scientist) to discuss Project design and potential biological concerns regarding the 7 Eureka Subsea Fiber Optic Cables Project (Project). Mr. O’Connell discussed the 8 importance of considering the western bumble bee. Ms. Flannery discussed the 9 importance of the hard ocean floor substrate and asked how the cable would be secured 10 to the ocean floor to reduce or eliminate scour. The western bumble bee has been 11 evaluated in the Biological Resources section of the main document, and direct and 12 indirect impacts are avoided. The Project Description describes in detail how the cable 13 would be installed on the ocean floor, the importance of the hard bottom substrate, and 14 the need for avoidance. 15 Consultation Outcomes: 16 • The Project was designed to avoid hard bottom substrate, and RTI Infrastructure 17 (RTI) conducted surveys of the ocean floor to ensure that proper routing of the 18 cable would occur. 19 • Ms. Flannery will be copied on all communications with the National Marine 20 Fisheries Service 21 California Department of Fish and Wildlife: On August 7, 2020, ICF held a conference 22 call with Greg O’Connell to discuss a site assessment and survey approach for the 23 western bumble bee. -
Vii Fishery-At-A-Glance: California Sheephead
Fishery-at-a-Glance: California Sheephead (Sheephead) Scientific Name: Semicossyphus pulcher Range: Sheephead range from the Gulf of California to Monterey Bay, California, although they are uncommon north of Point Conception. Habitat: Both adult and juvenile Sheephead primarily reside in kelp forest and rocky reef habitats. Size (length and weight): Male Sheephead can grow up to a length of three feet (91 centimeters) and weigh over 36 pounds (16 kilograms). Life span: The oldest Sheephead ever reported was a male at 53 years. Reproduction: As protogynous hermaphrodites, all Sheephead begin life as females, and older, larger females can develop into males. They are batch spawners, releasing eggs and sperm into the water column multiple times during their spawning season from July to September. Prey: Sheephead are generalist carnivores whose diet shifts throughout their growth. Juveniles primarily consume small invertebrates like tube-dwelling polychaetes, bryozoans and brittle stars, and adults shift to consuming larger mobile invertebrates like sea urchins. Predators: Predators of adult Sheephead include Giant Sea Bass, Soupfin Sharks and California Sea Lions. Fishery: Sheephead support both a popular recreational and a commercial fishery in southern California. Area fished: Sheephead are fished primarily south of Point Conception (Santa Barbara County) in nearshore waters around the offshore islands and along the mainland shore over rocky reefs and in kelp forests. Fishing season: Recreational anglers can fish for Sheephead from March 1through December 31 onboard boats south of Point Conception and May 1 through December 31 between Pigeon Point and Point Conception. Recreational divers and shore-based anglers can fish for Sheephead year round.