The Biological Resources Section Provides Background Information
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Egg-Mimics of Streptanthus (Cruciferae) Deter Oviposition by Pieris Sisymbrii (Lepidoptera: Pieridae)
Oecologia (Berl) (1981) 48:142-143 Oecologia Springer-Verlag 198l Short Communication Egg-Mimics of Streptanthus (Cruciferae) Deter Oviposition by Pieris sisymbrii (Lepidoptera: Pieridae) Arthur M. Shapiro Department of Zoology, University of California, Davis, CA 95616, USA Summary. Streptanthus breweri, a serpentine-soil annual mus- appear to decrease the attractiveness of mature S. glandulosus tard, produces pigmented callosities on its upper leaves which to ovipositing females (Shapiro, in press). are thought to mimic the eggs of the Pierid butterfly Pieris The efficacy of the suspected egg-mimics of S. breweri was sisymbrii. P. sisymbrii is one of several inflorescence - infructes- tested afield at Turtle Rock, Napa County, California (North cence-feeding Pierids which assess egg load visually on individual Coast Ranges). The site is an almost unvegetated, steep serpen- host plants prior to ovipositing. Removal of the "egg-mimics" tine talus slope with a S to SW exposure. S. breweri is the domi- from S. breweri plants in situ significantly increases the probabili- nant Crucifer (S. glandulosus also occurs) and P. sisymbrii the ty of an oviposition relative to similar, intact plants. dominant Pierid (Anthocharis sara Lucas and Euchloe hyantis Edw., both Euchloines, are present). On 10 April 1980 I prepared two lists of 50 numbers from a random numbers table. On 11 April, 100 plants of S. breweri "Egg-load assessment" occurs when a female insect's choice in the appropriate phenophase (elongating/budding, bearing egg- to oviposit or not on a given substrate is influenced by whether mimics) were numbered and tagged. Each was measured, its or not eggs (con or heterospecific) are present. -
"National List of Vascular Plant Species That Occur in Wetlands: 1996 National Summary."
Intro 1996 National List of Vascular Plant Species That Occur in Wetlands The Fish and Wildlife Service has prepared a National List of Vascular Plant Species That Occur in Wetlands: 1996 National Summary (1996 National List). The 1996 National List is a draft revision of the National List of Plant Species That Occur in Wetlands: 1988 National Summary (Reed 1988) (1988 National List). The 1996 National List is provided to encourage additional public review and comments on the draft regional wetland indicator assignments. The 1996 National List reflects a significant amount of new information that has become available since 1988 on the wetland affinity of vascular plants. This new information has resulted from the extensive use of the 1988 National List in the field by individuals involved in wetland and other resource inventories, wetland identification and delineation, and wetland research. Interim Regional Interagency Review Panel (Regional Panel) changes in indicator status as well as additions and deletions to the 1988 National List were documented in Regional supplements. The National List was originally developed as an appendix to the Classification of Wetlands and Deepwater Habitats of the United States (Cowardin et al.1979) to aid in the consistent application of this classification system for wetlands in the field.. The 1996 National List also was developed to aid in determining the presence of hydrophytic vegetation in the Clean Water Act Section 404 wetland regulatory program and in the implementation of the swampbuster provisions of the Food Security Act. While not required by law or regulation, the Fish and Wildlife Service is making the 1996 National List available for review and comment. -
Macroevolutionary Patterns of Glucosinolate Defense and Tests of Defense-Escalation and Resource Availability Hypotheses
Research Macroevolutionary patterns of glucosinolate defense and tests of defense-escalation and resource availability hypotheses N. Ivalu Cacho1,2, Daniel J. Kliebenstein3,4 and Sharon Y. Strauss1 1Center for Population Biology, and Department of Evolution of Ecology, University of California, One Shields Avenue, Davis, CA 95616, USA; 2Instituto de Biologıa, Universidad Nacional Autonoma de Mexico, Circuito Exterior, Ciudad Universitaria, 04510 Mexico City, Mexico; 3Department of Plant Sciences, University of California. One Shields Avenue, Davis, CA 95616, USA; 4DynaMo Center of Excellence, University of Copenhagen, Thorvaldsensvej 40, DK-1871 Frederiksberg C, Denmark Summary Author for correspondence: We explored macroevolutionary patterns of plant chemical defense in Streptanthus (Brassi- N. Ivalu Cacho caceae), tested for evolutionary escalation of defense, as predicted by Ehrlich and Raven’s Tel: +1 530 304 5391 plant–herbivore coevolutionary arms-race hypothesis, and tested whether species inhabiting Email: [email protected] low-resource or harsh environments invest more in defense, as predicted by the resource Received: 13 April 2015 availability hypothesis (RAH). Accepted: 8 June 2015 We conducted phylogenetically explicit analyses using glucosinolate profiles, soil nutrient analyses, and microhabitat bareness estimates across 30 species of Streptanthus inhabiting New Phytologist (2015) 208: 915–927 varied environments and soils. doi: 10.1111/nph.13561 We found weak to moderate phylogenetic signal in glucosinolate classes -
Suisun Marsh Tidal Marsh and Aquatic Habitats Conceptual Model
Suisun Marsh Tidal Marsh and Aquatic Habitats Conceptual Model References In-Progress DRAFT October 27, 2010 Suisun Marsh Habitat Management, Restoration and Preservation Plan IN-PROGRESS DRAFT References / Suisun Marsh Plan Tidal Marsh and Aquatic Habitats Conceptual Model Adams, P.B., C.B. Grimes, J.E. Hightower, S.T. Lindley, and M.L. Moser. 2002. Status Review for North American Green Sturgeon, Acipenser medirostris. National Marine Fisheries Service, Southwest Fisheries Science Center. 49 pages. Adams, P.B. 1990. Saltmarsh Ecology. Cambridge University Press. 473 pp. Albertson, J.D., and J. Evens. 2000. California clapper rail. In: Olofson, P.R. (ed.): Baylands Ecosystem Species and Community Profiles: life histories and environmental requirements of key plants, fish, and wildlife. Goals Project (Baylands Ecosystem Habitat Goals), San Francisco Bay Regional Water Quality Control Board, Oakland, California. Alberston, J. D. 1995. Ecology of the California clapper rail in South San Francisco Bay. M.S. Thesies, San Francisco State Univ. 200 pp. Allen. J.R.L. 2000. Morphodynamics of Holocene salt marshes: a review from the Atlantic and southern North Sea concepts of Europe. Quaternary Science Review 19(12):1155-1231. Allen, M.A. and T.J. Hassler. 1986. Species profiles: Life histories and environmental requirements of coastal fishes and invertebrates (Pacific Southwest) - Chinook salmon. Allen, P.J. and J. Cech, Jr. 2006. Age/size effects on juvenile green sturgeon, Acipensermedirostris, oxygen consumption, growth, and osmoregulation in saline environments Environ Biol Fish 79:211–229. Applegarth, J. H. 1938. The ecology of the California clapper rail in the south arm of the San Francisco Bay. -
Excerpt from the Steelhead Report Concerning Napa County (212
Historical Distribution and Current Status of Steelhead/Rainbow Trout (Oncorhynchus mykiss) in Streams of the San Francisco Estuary, California Robert A. Leidy, Environmental Protection Agency, San Francisco, CA Gordon S. Becker, Center for Ecosystem Management and Restoration, Oakland, CA Brett N. Harvey, John Muir Institute of the Environment, University of California, Davis, CA This report should be cited as: Leidy, R.A., G.S. Becker, B.N. Harvey. 2005. Historical distribution and current status of steelhead/rainbow trout (Oncorhynchus mykiss) in streams of the San Francisco Estuary, California. Center for Ecosystem Management and Restoration, Oakland, CA. Center for Ecosystem Management and Restoration NAPA COUNTY Huichica Creek Watershed The Huichica Creek watershed is in the southwest corner of Napa County. The creek flows in a generally southern direction into Hudeman Slough, which enters the Napa River via the Napa Slough. Huichica Creek consists of approximately eight miles of channel. Huichica Creek In March 1966 and in the winters of 1970 and 1971, DFG identified O. mykiss in Huichica Creek (Hallett and Lockbaum 1972; Jones 1966, as cited in Hallett, 1972). In December 1976, DFG visually surveyed Huichica Creek from the mouth to Route 121 and concluded that the area surveyed offered little or no value as spawning or nursery grounds for anadromous fish. However, the area was said to provide passage to more suitable areas upstream (Reed 1976). In January 1980, DFG visually surveyed Huichica Creek from Route 121 upstream to the headwaters. Oncorhynchus mykiss ranging from 75–150 mm in length were numerous and were estimated at a density of 10 per 30 meters (Ellison 1980). -
MONK & ASSOCIATES Environmental Consultants BIOLOGICAL RESOURCES CONSTRAINTS ANALYSIS the VERANDA at INDIAN SPRINGS 1522, 1
MONK & ASSOCIATES Environmental Consultants BIOLOGICAL RESOURCES CONSTRAINTS ANALYSIS THE VERANDA AT INDIAN SPRINGS 1522, 1510, 1506, 1502, 1504 LINCOLN AVE CALISTOGA, CALIFORNIA July 16, 2020 Prepared for Metropolitan Planning Group 1303 Jefferson Street, Suite 100-B Napa, California 94559 Attention: Ms. Olivia Ervin Prepared by Monk & Associates, Inc. 1136 Saranap Avenue, Suite Q Walnut Creek, California 94595 Contact: Ms. Sarah Lynch 1136 Saranap Ave., Suite Q Walnut Creek California 94595 (925) 947-4867 FAX (925) 947-1165 Biological Resources Constraints Analysis MONK & ASSOCIATES The Veranda at Indian Springs 1522, 1510, 1506, 1502, 1504 Lincoln Ave Calistoga, California APNs 011‐034‐003; ‐004; -005; ‐006; ‐021; ‐022; 028; ‐029 TABLE OF CONTENTS 1. INTRODUCTION ............................................................................................................................ 1 2. PROPOSED PROJECT .................................................................................................................... 1 3. STUDY METHODS ......................................................................................................................... 1 4. EXISTING SITE CONDITIONS AND SURROUNDING LAND USES .................................... 2 4.1 Evaluation for Waters of the U.S. and Waters of the State .................................................... 3 4.1.1 APPLICABILITY TO THE PROJECT SITE..................................................................................... 3 5. SPECIAL-STATUS SPECIES ISSUES ......................................................................................... -
Streptanthus Morrisonii</Em&G
Butler University Digital Commons @ Butler University Scholarship and Professional Work - LAS College of Liberal Arts & Sciences 1989 Taxonomy of Streptanthus sect. Biennes, the Streptanthus morrisonii complex (Brassicaceae) Rebecca W. Dolan Butler University, [email protected] Lawrence F. LaPre Follow this and additional works at: https://digitalcommons.butler.edu/facsch_papers Part of the Botany Commons, and the Ecology and Evolutionary Biology Commons Recommended Citation Dolan, Rebecca W. and LaPre, Lawrence F., "Taxonomy of Streptanthus sect. Biennes, the Streptanthus morrisonii complex (Brassicaceae)" Madroño / (1989): 33-40. Available at https://digitalcommons.butler.edu/facsch_papers/45 This Article is brought to you for free and open access by the College of Liberal Arts & Sciences at Digital Commons @ Butler University. It has been accepted for inclusion in Scholarship and Professional Work - LAS by an authorized administrator of Digital Commons @ Butler University. For more information, please contact [email protected]. Permission to post this publication in our archive was granted by the copyright holder, Berkeley, California Botanical Society, 1916- (http://www.calbotsoc.org/madrono.html). This copy should be used for educational and research purposes only. The original publication appeared at: Dolan, R.W. and L.F. LaPre'. 1989. Taxonomy of Streptanthus sect. Biennes, the Streptanthus morrisonii complex. (Brassicaceae). Madroño 36:33-40. DOI: not available TAXONOMY OF STREPTANTHUS SECT. BIENNES, THE STREPTANTHUS MORRISONll COMPLEX (BRASSICACEAE) REBECCA W. DOLAN Holcomb Research Institute and Biological Sciences Department, Butler University, 4600 Sunset Avenue, Indianapolis, IN 46208 LAWRENCE F. LAPRE Tierra Madre Consultants, 4178 Chestnut Street, Riverside, CA 92501 ABSTRACT The S/reptanthus morrisonii complex is a six-taxon group of closely related ser pentine rock outcrop endemics from Lake, Napa, and Sonoma counties ofCalifornia, USA. -
Butte Co. Meadowfoam
U.S. Fish and Wildlife Service, and the U.S. Air Force, respectively. All of the Fort Ord occurrences are on land within the Habitat Management Plan Habitat Reserve lands and will be conserved and managed in perpetuity (W. Collins in litt. 2005; U.S. Army Corps of Engineers 1997). The population at Travis Air Force Base, including over 20 acres of adjacent restored vernal pools, is protected as a special ecological preserve, with protective measures and appropriate management for the species provided in the Travis Air Force Base Land Management Plan. Seasonal managed cattle grazing has been returned to two conservation sites supporting Lasthenia conjugens: 1) the Warm Springs Seasonal Wetland Unit of the Don Edwards San Francisco Bay National Wildlife Refuge in Alameda County, and 2) the State Route 4 Preserve managed by the Muir Heritage Land Trust in Contra Costa County. The L. conjugens population at the Warm Springs Unit has declined during the last 10 years due to many factors including competition by nonnative plant species. During this time period, grazing, which occurred intermittently at the Warm Springs Unit since the 1800s, has been excluded by the Refuge until a management plan could be developed. The decline in the L. conjugens population at the Warm Springs Unit cannot be attributed to a single factor, but most likely results from the complex interaction of several variables including current and historical land uses, the abiotic environment, and annual climatic variation. The increasing dominance of nonnative grasses, however, coincides with the suspension of livestock grazing, suggesting that the lack of a disturbance regime may be a primary factor in the degradation of habitat for L. -
Tidal Marsh Recovery Plan Habitat Creation Or Enhancement Project Within 5 Miles of OAK
U.S. Fish & Wildlife Service Recovery Plan for Tidal Marsh Ecosystems of Northern and Central California California clapper rail Suaeda californica Cirsium hydrophilum Chloropyron molle Salt marsh harvest mouse (Rallus longirostris (California sea-blite) var. hydrophilum ssp. molle (Reithrodontomys obsoletus) (Suisun thistle) (soft bird’s-beak) raviventris) Volume II Appendices Tidal marsh at China Camp State Park. VII. APPENDICES Appendix A Species referred to in this recovery plan……………....…………………….3 Appendix B Recovery Priority Ranking System for Endangered and Threatened Species..........................................................................................................11 Appendix C Species of Concern or Regional Conservation Significance in Tidal Marsh Ecosystems of Northern and Central California….......................................13 Appendix D Agencies, organizations, and websites involved with tidal marsh Recovery.................................................................................................... 189 Appendix E Environmental contaminants in San Francisco Bay...................................193 Appendix F Population Persistence Modeling for Recovery Plan for Tidal Marsh Ecosystems of Northern and Central California with Intial Application to California clapper rail …............................................................................209 Appendix G Glossary……………......................................................................………229 Appendix H Summary of Major Public Comments and Service -
Chinese Mitten Crab (Eriocheir Sinensis) in San Francisco Bay
Distribution, Ecology and Potential Impacts of the Chinese Mitten Crab (Eriocheir sinensis) in San Francisco Bay Deborah A Rudnick Kathleen M. Halat Vincent H. Resh Department of Environmental Science, Policy and Management University of California, Berkeley TECHNICAL COMPLETION REPORT Project Number: UCAL-WRC-W-881 University of California Water Resources Center Contribution #206 ISBN 1-887192-12-3 June 2000 The University of California prohibits discrimination against or harassment of any person employed by or seeking employment with the University on the basis of race, color, national origin, religion, sex, physical or mental disability, medical condition (cancer- related), ancestry, marital status, age, sexual orientation, citizenship or status as a Vietnam-era veteran or special disabled veteran. The University of California is an affirmative action/equal opportunity employer. The University undertakes affirmative action to assure equal employment opportunity for underutilized minorities and women, for persons with disabilities, and for Vietnam-era veterans and special disabled veterans. University policy is intended to be consistent with the provisions of applicable State and Federal law. Inquiries regarding this policy may be addressed to the Affirmative Action Director, University of California, Agriculture and Natural Resources, 300 Lakeside Drive, 6th Floor, Oakland, CA 94612-3560, (510) 987-0097. This publication is a continuation in the Water Resources Center Contribution series. It is published and distributed by the UNIVERSITY -
The Southern California Wetlands Recovery Project’S Regional Strategy
Developing a Science-based, Management- driven Plan for Restoring Wetlands: The Southern California Wetlands Recovery Project’s Regional Strategy Carolyn Lieberman U.S. Fish and Wildlife Service Coastal Program Mediterranean Climate Average Monthly Temperature at Lindbergh Field, San Diego 80 70 60 50 40 30 Temperature (*F) Temperature 20 10 0 JAN FEB MAR APR MAY JUN JUL AUG SEP OCT NOV DEC Month Average Monthly Rainfall at Lindbergh Field, San Diego 2 1.8 1.6 1.4 1.2 1 0.8 Rainfall Rainfall (inches) 0.6 0.4 0.2 0 JAN FEB MAR APR MAY JUN JUL AUG SEP OCT NOV DEC Month Based on data from 1948-1990 (http://www.wrh.noaa.gov/sgx/climate/san-san.htm) Coastal Wetland Systems of Southern California • Approximately 100 distinct systems • Total of 8,237 ha • Range = 0.03 ha – 1,322 ha – Average size = 81 ha Small Creek Mouth Systems Bell Canyon Arroyo Burro Intermittently Closing River Mouth Estuaries Malibu Lagoon Open Basin, Fringing Intertidal Wetland Anaheim Bay and Seal Beach Large Depositional River Valley Tijuana River Valley Harbors, Bay, Lagoons Mission Bay Mission Bay San Diego Bay Sensitive Species in Coastal Estuaries Ridgway’s rail Western snowy plover Belding’s savannah sparrow Salt marsh bird’s beak Light-footed clapper rail California least tern Migratory Birds Southern California Wetland Recovery Project Federal Partners National Marine Fisheries Service Natural Resources Conservation Service U.S. Army Corps of Engineers U.S. Environmental Protection Agency U.S. Fish and Wildlife Service State Partners California Natural Resources -
Southern Coastal Santa Barbara Streams and Estuaries Bioassessment Program
SOUTHERN COASTAL SANTA BARBARA STREAMS AND ESTUARIES BIOASSESSMENT PROGRAM 2014 REPORT AND UPDATED INDEX OF BIOLOGICAL INTEGRITY Prepared for: City of Santa Barbara, Creeks Division County of Santa Barbara, Project Clean Water Prepared By: www.ecologyconsultantsinc.com Ecology Consultants, Inc. Executive Summary Introduction This report summarizes the results of the 2014 Southern Coastal Santa Barbara Streams and Estuaries Bioassessment Program, an effort funded by the City of Santa Barbara and County of Santa Barbara. This is the 15th year of the Program, which began in 2000. Ecology Consultants, Inc. (Ecology) prepared this report, and serves as the City and County’s consultant for the Program. The purpose of the Program is to assess and monitor the “biological integrity” of study streams and estuaries as they respond through time to natural and human influences. The Program involves annual collection and analyses of benthic macroinvertebrate (BMI) samples and other pertinent physiochemical and biological data at study streams using U.S. Environmental Protection Agency (USEPA) endorsed rapid bioassessment methodology. BMI samples are analyzed in the laboratory to determine BMI abundance, composition, and diversity. Scores and classifications of biological integrity are determined for study streams using the BMI based Index of Biological Integrity (IBI) constructed by Ecology. The IBI was initially built in 2004, updated in 2009, and has been updated again this year. The IBI yields a numeric score and classifies the biological integrity of a given stream as Very Poor, Poor, Fair, Good, or Excellent based on the contents of the BMI sample collected from the stream. Several “core metrics” are calculated and used to determine the IBI score.