Fish and Wildlife in the Corte Madera Creek Watershed
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Pleuronectidae, Poecilopsettidae, Achiridae, Cynoglossidae
1536 Glyptocephalus cynoglossus (Linnaeus, 1758) Pleuronectidae Witch flounder Range: Both sides of North Atlantic Ocean; in the western North Atlantic from Strait of Belle Isle to Cape Hatteras Habitat: Moderately deep water (mostly 45–330 m), deepest in southern part of range; found on mud, muddy sand or clay substrates Spawning: May–Oct in Gulf of Maine; Apr–Oct on Georges Bank; Feb–Jul Meristic Characters in Middle Atlantic Bight Myomeres: 58–60 Vertebrae: 11–12+45–47=56–59 Eggs: – Pelagic, spherical Early eggs similar in size Dorsal fin rays: 97–117 – Diameter: 1.2–1.6 mm to those of Gadus morhua Anal fin rays: 86–102 – Chorion: smooth and Melanogrammus aeglefinus Pectoral fin rays: 9–13 – Yolk: homogeneous Pelvic fin rays: 6/6 – Oil globules: none Caudal fin rays: 20–24 (total) – Perivitelline space: narrow Larvae: – Hatching occurs at 4–6 mm; eyes unpigmented – Body long, thin and transparent; preanus length (<33% TL) shorter than in Hippoglossoides or Hippoglossus – Head length increases from 13% SL at 6 mm to 22% SL at 42 mm – Body depth increases from 9% SL at 6 mm to 30% SL at 42 mm – Preopercle spines: 3–4 occur on posterior edge, 5–6 on lateral ridge at about 16 mm, increase to 17–19 spines – Flexion occurs at 14–20 mm; transformation occurs at 22–35 mm (sometimes delayed to larger sizes) – Sequence of fin ray formation: C, D, A – P2 – P1 – Pigment intensifies with development: 6 bands on body and fins, 3 major, 3 minor (see table below) Glyptocephalus cynoglossus Hippoglossoides platessoides Total myomeres 58–60 44–47 Preanus length <33%TL >35%TL Postanal pigment bars 3 major, 3 minor 3 with light scattering between Finfold pigment Bars extend onto finfold None Flexion size 14–20 mm 9–19 mm Ventral pigment Scattering anterior to anus Line from anus to isthmus Early Juvenile: Occurs in nursery habitats on continental slope E. -
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. -
Communal Roosting Behavior and Winter Diet of the White-Tailed Kite (Elanus Leucurus) in an Agricultural Habitat on the Argentine Pampas
J. Raptor Res. 44(3):202–207 E 2010 The Raptor Research Foundation, Inc. COMMUNAL ROOSTING BEHAVIOR AND WINTER DIET OF THE WHITE-TAILED KITE (ELANUS LEUCURUS) IN AN AGRICULTURAL HABITAT ON THE ARGENTINE PAMPAS JOSE´ HERNA´ N SARASOLA,1 CLAUDINA SOLARO, AND MIGUEL A´ NGEL SANTILLA´ N Centro para el Estudio y Conservacio´n de las Aves Rapaces en Argentina (CECARA), Universidad Nacional de La Pampa – CONICET, Avda. Uruguay 151, 6300 Santa Rosa, La Pampa, Argentina MAXIMILIANO ADRIA´ N GALMES Centro para el Estudio y Conservacio´n de las Aves Rapaces en Argentina (CECARA), Universidad Nacional de La Pampa – CONICET, Avda. Uruguay 151, 6300 Santa Rosa, La Pampa, Argentina and The Peregrine Fund, 5668 West Flying Hawk Lane, Boise, ID 83709 U.S.A. ABSTRACT.—Although the White-tailed Kite (Elanus leucurus) is widely distributed throughout the Americas, winter communal roosting has been recorded only in the Nearctic portion of its range. As a result, data on the food habits of the White-tailed Kite in South America during the nonbreeding season are scarce and, when available, limited to pellets from solitary individuals. Here, we report the communal roosting behav- ior and the winter diet of White-tailed Kites in an agricultural habitat on the Argentine pampas based on information gathered over three consecutive years (2006–2008). From May to July of each year, we observed an average of 11 (6SD 5 2.8) kites roosting in a grove of Eucalyptus viminalis. Prior to roosting, kites gathered in a tall, dead, and leafless Eucalyptus tree before flying to more densely foliated trees where they spent the night. -
Population Analysis and Community Workshop for Far Eastern Curlew Conservation Action in Pantai Cemara, Desa Sungai Cemara – Jambi
POPULATION ANALYSIS AND COMMUNITY WORKSHOP FOR FAR EASTERN CURLEW CONSERVATION ACTION IN PANTAI CEMARA, DESA SUNGAI CEMARA – JAMBI Final Report Small Grant Fund of the EAAFP Far Eastern Curlew Task Force Iwan Febrianto, Cipto Dwi Handono & Ragil S. Rihadini Jambi, Indonesia 2019 The aim of this project are to Identify the condition of Far Eastern Curlew Population and the remaining potential sites for Far Eastern Curlew stopover in Sumatera, Indonesia and protect the remaining stopover sites for Far Eastern Curlew by educating the government, local people and community around the sites as the effort of reducing the threat of habitat degradation, habitat loss and human disturbance at stopover area. INTRODUCTION The Far Eastern Curlew (Numenius madagascariencis) is the largest shorebird in the world and is endemic to East Asian – Australian Flyway. It is one of the Endangered migratory shorebird with estimated global population at 38.000 individual, although a more recent update now estimates the population at 32.000 (Wetland International, 2015 in BirdLife International, 2017). An analysis of monitoring data collected from around Australia and New Zealand (Studds et al. in prep. In BirdLife International, 2017) suggests that the species has declined much more rapidly than was previously thought; with an annual rate of decline of 0.058 equating to a loss of 81.7% over three generations. Habitat loss occuring as a result of development is the most significant threat currently affecting migratory shorebird along the EAAF (Melville et al. 2016 in EAAFP 2017). Loss of habitat at critical stopover sites in the Yellow Sea is suspected to be the key threat to this species and given that it is restricted to East Asian - Australasian Flyway, the declines in the non-breeding are to be representative of the global population. -
3.8 Biological Resources
Section 3.8 – Biological Resources 3.8 BIOLOGICAL RESOURCES 3.8.1 INTRODUCTION The purpose of this section is to identify existing biological resources within the planning area covered by the proposed project, analyze potential biological impacts, and recommend mitigation measures to avoid or lessen the significance of any identified adverse impacts. The assessment of impacts to biological resources is a qualitative review of the existing biological resources within the City and its SOI and a determination of whether the proposed project includes adequate provisions to ensure the protection of these resources. Given the programmatic nature of the PEIR, specific impacts to individual properties or areas are not identified or known at this time. 3.8.2 ENVIRONMENTAL SETTING The information contained in this Environmental Setting section is primarily from information contained in the City of Lake Elsinore General Plan Background Reports (see Chapter 3 – Biological Resources). This document is attached as Appendix B to this PEIR. The City and SOI are located in the Elsinore Valley, which is generally bounded on the west by the east flank of the rugged Santa Ana Mountains and on the west by gently sloping hills. The San Jacinto River and Temescal Wash cut through the valley, converging at Lake Elsinore. The area contains a mixture of land developed for residential, commercial, industrial, recreational, and agricultural uses and undeveloped land remaining in its natural state. Approximately 16 natural vegetative communities, in addition to developed sites and agricultural uses, occur in the City and its SOI. Each of these habitats provides cover, food, and water necessary to meet biological requirements of a variety of animal species. -
Draft Version Target Shorebird Species List
Draft Version Target Shorebird Species List The target species list (species to be surveyed) should not change over the course of the study, therefore determining the target species list is an important project design task. Because waterbirds, including shorebirds, can occur in very high numbers in a census area, it is often not possible to count all species without compromising the quality of the survey data. For the basic shorebird census program (protocol 1), we recommend counting all shorebirds (sub-Order Charadrii), all raptors (hawks, falcons, owls, etc.), Common Ravens, and American Crows. This list of species is available on our field data forms, which can be downloaded from this site, and as a drop-down list on our online data entry form. If a very rare species occurs on a shorebird area survey, the species will need to be submitted with good documentation as a narrative note with the survey data. Project goals that could preclude counting all species include surveys designed to search for color-marked birds or post- breeding season counts of age-classed bird to obtain age ratios for a species. When conducting a census, you should identify as many of the shorebirds as possible to species; sometimes, however, this is not possible. For example, dowitchers often cannot be separated under censuses conditions, and at a distance or under poor lighting, it may not be possible to distinguish some species such as small Calidris sandpipers. We have provided codes for species combinations that commonly are reported on censuses. Combined codes are still species-specific and you should use the code that provides as much information as possible about the potential species combination you designate. -
Birds of the East Texas Baptist University Campus with Birds Observed Off-Campus During BIOL3400 Field Course
Birds of the East Texas Baptist University Campus with birds observed off-campus during BIOL3400 Field course Photo Credit: Talton Cooper Species Descriptions and Photos by students of BIOL3400 Edited by Troy A. Ladine Photo Credit: Kenneth Anding Links to Tables, Figures, and Species accounts for birds observed during May-term course or winter bird counts. Figure 1. Location of Environmental Studies Area Table. 1. Number of species and number of days observing birds during the field course from 2005 to 2016 and annual statistics. Table 2. Compilation of species observed during May 2005 - 2016 on campus and off-campus. Table 3. Number of days, by year, species have been observed on the campus of ETBU. Table 4. Number of days, by year, species have been observed during the off-campus trips. Table 5. Number of days, by year, species have been observed during a winter count of birds on the Environmental Studies Area of ETBU. Table 6. Species observed from 1 September to 1 October 2009 on the Environmental Studies Area of ETBU. Alphabetical Listing of Birds with authors of accounts and photographers . A Acadian Flycatcher B Anhinga B Belted Kingfisher Alder Flycatcher Bald Eagle Travis W. Sammons American Bittern Shane Kelehan Bewick's Wren Lynlea Hansen Rusty Collier Black Phoebe American Coot Leslie Fletcher Black-throated Blue Warbler Jordan Bartlett Jovana Nieto Jacob Stone American Crow Baltimore Oriole Black Vulture Zane Gruznina Pete Fitzsimmons Jeremy Alexander Darius Roberts George Plumlee Blair Brown Rachel Hastie Janae Wineland Brent Lewis American Goldfinch Barn Swallow Keely Schlabs Kathleen Santanello Katy Gifford Black-and-white Warbler Matthew Armendarez Jordan Brewer Sheridan A. -
Greenland Turbot Assessment
6HFWLRQ STOCK ASSESSMENT OF GREENLAND TURBOT James N. Ianelli, Thomas K. Wilderbuer, and Terrance M. Sample 6XPPDU\ Changes to this year’s assessment in the past year include: 1. new summary estimates of retained and discarded Greenland turbot by different target fisheries, 2. update the estimated catch levels by gear type in recent years, and 3. new length frequency and biomass data from the 1998 NMFS eastern Bering Sea shelf survey. Conditions do not appear to have changed substantively over the past several years. For example, the abundance of Greenland turbot from the eastern Bering Sea (EBS) shelf-trawl survey has found only spotty quantities with very few small fish that were common in the late 1970s and early 1980s. The majority of the catch has shifted to longline gear in recent years. The assessment model analysis was similar to last year but with a slightly higher estimated overall abundance. We attribute this to a slightly improved fit to the longline survey data trend. The target stock size (B40%, female spawning biomass) is estimated at about 139,000 tons while the projected 1999 spawning biomass is about 110,000 tons. The adjusted yield projection from F40% computations is estimated at 20,000 tons for 1999, and increase of 5,000 from last year’s ABC. Given the continued downward abundance trend and no sign of recruitment to the EBS shelf, extra caution is warranted. We therefore recommend that the ABC be set to 15,000 tons (same value as last year). As additional survey information become available and signs of recruitment (perhaps from areas other than the shelf) are apparent, then we believe that the full ABC or increases in harvest may be appropriate for this species. -
A Classification of the Rallidae
A CLASSIFICATION OF THE RALLIDAE STARRY L. OLSON HE family Rallidae, containing over 150 living or recently extinct species T and having one of the widest distributions of any family of terrestrial vertebrates, has, in proportion to its size and interest, received less study than perhaps any other major group of birds. The only two attempts at a classifi- cation of all of the recent rallid genera are those of Sharpe (1894) and Peters (1934). Although each of these lists has some merit, neither is satisfactory in reflecting relationships between the genera and both often separate closely related groups. In the past, no attempt has been made to identify the more primitive members of the Rallidae or to illuminate evolutionary trends in the family. Lists almost invariably begin with the genus Rdus which is actually one of the most specialized genera of the family and does not represent an ancestral or primitive stock. One of the difficulties of rallid taxonomy arises from the relative homo- geneity of the family, rails for the most part being rather generalized birds with few groups having morphological modifications that clearly define them. As a consequence, particularly well-marked genera have been elevated to subfamily rank on the basis of characters that in more diverse families would not be considered as significant. Another weakness of former classifications of the family arose from what Mayr (194933) referred to as the “instability of the morphology of rails.” This “instability of morphology,” while seeming to belie what I have just said about homogeneity, refers only to the characteristics associated with flightlessness-a condition that appears with great regularity in island rails and which has evolved many times. -
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 -
CONVERGENT EVOLUTION of ELANUS KITES and the OWLS Author(S): Juan J
CONVERGENT EVOLUTION OF ELANUS KITES AND THE OWLS Author(s): Juan J. Negro, Cino Pertoldi, Ettore Randi, Juan J. Ferrero, José M. López-Caballero, Domingo Rivera, and Erkki Korpimäki Source: Journal of Raptor Research, 40(3):222-225. 2006. Published By: The Raptor Research Foundation DOI: 10.3356/0892-1016(2006)40[222:CEOEKA]2.0.CO;2 URL: http://www.bioone.org/doi/full/10.3356/0892- 1016%282006%2940%5B222%3ACEOEKA%5D2.0.CO%3B2 BioOne (www.bioone.org) is an electronic aggregator of bioscience research content, and the online home to over 160 journals and books published by not-for-profit societies, associations, museums, institutions, and presses. Your use of this PDF, the BioOne Web site, and all posted and associated content indicates your acceptance of BioOne’s Terms of Use, available at www.bioone.org/page/terms_of_use. Usage of BioOne content is strictly limited to personal, educational, and non-commercial use. Commercial inquiries or rights and permissions requests should be directed to the individual publisher as copyright holder. BioOne sees sustainable scholarly publishing as an inherently collaborative enterprise connecting authors, nonprofit publishers, academic institutions, research libraries, and research funders in the common goal of maximizing access to critical research. SHORT COMMUNICATIONS J. Raptor Res. 40(3):222–225 E 2006 The Raptor Research Foundation, Inc. CONVERGENT EVOLUTION OF ELANUS KITES AND THE OWLS JUAN J. NEGRO1 AND CINO PERTOLDI Estacio´n Biolo´gica de Don˜ana, Apdo. 1056, 41080 Sevilla, Spain ETTORE RANDI Istituto Nazionale per la Fauna Selvatica, 40064 Ozzano Emilia (BO), Italy JUAN J. -
The Status and Occurrence of Black Phoebe (Sayornis Nigricans) in British Columbia
The Status and Occurrence of Black Phoebe (Sayornis nigricans) in British Columbia. By Rick Toochin. Introduction and Distribution The Black Phoebe (Sayornis nigricans) is a small passerine belonging to the tyrant-flycatcher family. The Black Phoebe occurs as a year-round resident throughout most of its range; however, its northern populations are partially migratory (Wahl et al. 2005). It is a species found throughout the year from southwestern Oregon south, through California including the Baja Peninsula (excluding the central regions of the Peninsula), east through Arizona, New Mexico, southern Colorado, west Texas, south through Mexico, Central America to Panama (excluding El Salvador) and in South America from the coastal mountains of Venezuela, through Colombia, Ecuador, and Peru, to western Bolivia and northwestern Argentina (Sibley 2000, Howell and Webb 2010, Hoyo et al. 2006). In the past couple of decades the Black Phoebe has been slowly expanding its known range northward into northern Oregon and southern Washington where it is still considered a very rare visitor, but with records increasing every year (Wahl et al. 2005, WBRC 2012). The Black Phoebe has been recorded from Idaho, Nevada, Utah, southern Oklahoma and Florida (Sibley 2000). The Black Phoebe is an accidental visitor to south-central Alaska (Gibson et al. 2013). In British Columbia this species is considered a casual visitor but Provincial records, like those of Washington State, are on the rise and the status of this species in British Columbia could change in the near future. Identification and Similar Species The Black Phoebe has a huge range that encompasses two continents.