UNIVERSITY of CALIFORNIA RIVERSIDE Understanding The
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Literature Cited
Literature Cited Robert W. Kiger, Editor This is a consolidated list of all works cited in volumes 19, 20, and 21, whether as selected references, in text, or in nomenclatural contexts. In citations of articles, both here and in the taxonomic treatments, and also in nomenclatural citations, the titles of serials are rendered in the forms recommended in G. D. R. Bridson and E. R. Smith (1991). When those forms are abbre- viated, as most are, cross references to the corresponding full serial titles are interpolated here alphabetically by abbreviated form. In nomenclatural citations (only), book titles are rendered in the abbreviated forms recommended in F. A. Stafleu and R. S. Cowan (1976–1988) and F. A. Stafleu and E. A. Mennega (1992+). Here, those abbreviated forms are indicated parenthetically following the full citations of the corresponding works, and cross references to the full citations are interpolated in the list alphabetically by abbreviated form. Two or more works published in the same year by the same author or group of coauthors will be distinguished uniquely and consistently throughout all volumes of Flora of North America by lower-case letters (b, c, d, ...) suffixed to the date for the second and subsequent works in the set. The suffixes are assigned in order of editorial encounter and do not reflect chronological sequence of publication. The first work by any particular author or group from any given year carries the implicit date suffix “a”; thus, the sequence of explicit suffixes begins with “b”. Works missing from any suffixed sequence here are ones cited elsewhere in the Flora that are not pertinent in these volumes. -
Moths & Butterflies of Grizzly Peak Preserve
2018 ANNUAL REPORT MOTHS & BUTTERFLIES OF GRIZZLY PEAK PRESERVE: Inventory Results from 2018 Prepared and Submi�ed by: DANA ROSS (Entomologist/Lepidoptera Specialist) Corvallis, Oregon SUMMARY The Grizzly Peak Preserve was sampled for butterflies and moths during May, June and October, 2018. A grand total of 218 species were documented and included 170 moths and 48 butterflies. These are presented as an annotated checklist in the appendix of this report. Butterflies and day-flying moths were sampled during daylight hours with an insect net. Nocturnal moths were collected using battery-powered backlight traps over single night periods at 10 locations during each monthly visit. While many of the documented butterflies and moths are common and widespread species, others - that include the Western Sulphur (Colias occidentalis primordialis) and the noctuid moth Eupsilia fringata - represent more locally endemic and/or rare taxa. One geometrid moth has yet to be identified and may represent an undescribed (“new”) species. Future sampling during March, April, July, August and September will capture many more Lepidoptera that have not been recorded. Once the site is more thoroughly sampled, the combined Grizzly Peak butterfly-moth fauna should total at least 450-500 species. INTRODUCTION The Order Lepidoptera (butterflies and moths) is an abundant and diverse insect group that performs essential ecological functions within terrestrial environments. As a group, these insects are major herbivores (caterpillars) and pollinators (adults), and are a critical food source for many species of birds, mammals (including bats) and predacious and parasitoid insects. With hundreds of species of butterflies and moths combined occurring at sites with ample habitat heterogeneity, a Lepidoptera inventory can provide a valuable baseline for biodiversity studies. -
APPENDIX D Biological Technical Report
APPENDIX D Biological Technical Report CarMax Auto Superstore EIR BIOLOGICAL TECHNICAL REPORT PROPOSED CARMAX AUTO SUPERSTORE PROJECT CITY OF OCEANSIDE, SAN DIEGO COUNTY, CALIFORNIA Prepared for: EnviroApplications, Inc. 2831 Camino del Rio South, Suite 214 San Diego, California 92108 Contact: Megan Hill 619-291-3636 Prepared by: 4629 Cass Street, #192 San Diego, California 92109 Contact: Melissa Busby 858-334-9507 September 29, 2020 Revised March 23, 2021 Biological Technical Report CarMax Auto Superstore TABLE OF CONTENTS EXECUTIVE SUMMARY ................................................................................................ 3 SECTION 1.0 – INTRODUCTION ................................................................................... 6 1.1 Proposed Project Location .................................................................................... 6 1.2 Proposed Project Description ............................................................................... 6 SECTION 2.0 – METHODS AND SURVEY LIMITATIONS ............................................ 8 2.1 Background Research .......................................................................................... 8 2.2 General Biological Resources Survey .................................................................. 8 2.3 Jurisdictional Delineation ...................................................................................... 9 2.3.1 U.S. Army Corps of Engineers Jurisdiction .................................................... 9 2.3.2 Regional Water Quality -
References and Appendices
References Ainley, D.G., S.G. Allen, and L.B. Spear. 1995. Off- Arnold, R.A. 1983. Ecological studies on six endan- shore occurrence patterns of marbled murrelets gered butterflies (Lepidoptera: Lycaenidae): in central California. In: C.J. Ralph, G.L. Hunt island biogeography, patch dynamics, and the Jr., M.G. Raphael, and J.F. Piatt, technical edi- design of habitat preserves. University of Cali- tors. Ecology and Conservation of the Marbled fornia Publications in Entomology 99: 1–161. Murrelet. USDA Forest Service, General Techni- Atwood, J.L. 1993. California gnatcatchers and coastal cal Report PSW-152; 361–369. sage scrub: the biological basis for endangered Allen, C.R., R.S. Lutz, S. Demairais. 1995. Red im- species listing. In: J.E. Keeley, editor. Interface ported fire ant impacts on Northern Bobwhite between ecology and land development in Cali- populations. Ecological Applications 5: 632-638. fornia. Southern California Academy of Sciences, Allen, E.B., P.E. Padgett, A. Bytnerowicz, and R.A. Los Angeles; 149–169. Minnich. 1999. Nitrogen deposition effects on Atwood, J.L., P. Bloom, D. Murphy, R. Fisher, T. Scott, coastal sage vegetation of southern California. In T. Smith, R. Wills, P. Zedler. 1996. Principles of A. Bytnerowicz, M.J. Arbaugh, and S. Schilling, reserve design and species conservation for the tech. coords. Proceedings of the international sym- southern Orange County NCCP (Draft of Oc- posium on air pollution and climate change effects tober 21, 1996). Unpublished manuscript. on forest ecosystems, February 5–9, 1996, River- Austin, M. 1903. The Land of Little Rain. University side, CA. -
Western Riverside County Multiple Species Habitat Conservation Plan (MSHCP) Biological Monitoring Program Rare Plant Survey Repo
Western Riverside County Multiple Species Habitat Conservation Plan (MSHCP) Biological Monitoring Program Rare Plant Survey Report 2008 15 April 2009 TABLE OF CONTENTS INTRODUCTION ............................................................................................................................1 SURVEY GOALS: ...........................................................................................................................1 METHODS .......................................................................................................................................2 PROTOCOL DEVELOPMENT............................................................................................................2 PERSONNEL AND TRAINING...........................................................................................................2 SURVEY SITE SELECTION ..............................................................................................................3 SURVEY METHODS........................................................................................................................7 DATA ANALYSIS ...........................................................................................................................9 RESULTS .......................................................................................................................................11 ALLIUM MARVINII, YUCAIPA ONION..............................................................................................13 ALLIUM MUNZII, MUNZ’S ONION -
Lepidoptera: Noctuidae) of Australia and Utility of DNA Barcodes for Pest Identification in Helicoverpa and Relatives
RESEARCH ARTICLE DNA Barcoding the Heliothinae (Lepidoptera: Noctuidae) of Australia and Utility of DNA Barcodes for Pest Identification in Helicoverpa and Relatives Andrew Mitchell1*, David Gopurenko2,3 1 Australian Museum Research Institute, Australian Museum, Sydney, NSW, Australia, 2 NSW Department of Primary Industries, Wagga Wagga, NSW, Australia, 3 Graham Centre for Agricultural Innovation, Wagga a11111 Wagga, NSW, Australia * [email protected] Abstract ’ OPEN ACCESS Helicoverpa and Heliothis species include some of the world s most significant crop pests, causing billions of dollars of losses globally. As such, a number are regulated quarantine Citation: Mitchell A, Gopurenko D (2016) DNA species. For quarantine agencies, the most crucial issue is distinguishing native species Barcoding the Heliothinae (Lepidoptera: Noctuidae) of Australia and Utility of DNA Barcodes for Pest from exotics, yet even this task is often not feasible because of poorly known local faunas Identification in Helicoverpa and Relatives. PLoS and the difficulties of identifying closely related species, especially the immature stages. ONE 11(8): e0160895. doi:10.1371/journal. DNA barcoding is a scalable molecular diagnostic method that could provide the solution to pone.0160895 this problem, however there has been no large-scale test of the efficacy of DNA barcodes Editor: Daniel Doucet, Natural Resources Canada, for identifying the Heliothinae of any region of the world to date. This study fills that gap by CANADA DNA barcoding the entire heliothine moth fauna of Australia, bar one rare species, and com- Received: May 6, 2016 paring results with existing public domain resources. We find that DNA barcodes provide Accepted: July 26, 2016 robust discrimination of all of the major pest species sampled, but poor discrimination of Published: August 10, 2016 Australian Heliocheilus species, and we discuss ways to improve the use of DNA barcodes for identification of pests. -
Big Tarplant (Blepharizonia Plumosa)
Plants Big Tarplant (Blepharizonia plumosa) Big Tarplant (Blepharizonia plumosa) Status Federal: None State: None CNPS: List 1B Population Trend Global: Unknown State: Unknown Within Inventory Area: Unknown © 2002 John Game Data Characterization The location database for big tarplant includes 36 data records dated from 1916 to 2001 (California Natural Diversity Database 2005). Twenty-nine of the occurrences were documented within the last 10 years. Seven of the occurrences have not been observed for over 60 years, but all the other occurrences are believed to be extant (California Natural Diversity Database 2005). Most of the occurrences are of high precision and may be accurately located, including those within the inventory area. Very little ecological information is available for big tarplant. The published literature on the species pertains primarily to its taxonomy. The main sources of general information on this species are the Jepson Manual (Hickman 1993) and the California Native Plant Society (2005). Specific observations on habitat and plant associates, threats, and other factors are summarized in the California Natural Diversity Database (2005). Range Big tarplant is endemic to the Mount Diablo foothills and is found primarily in eastern Contra Costa, eastern Alameda, and western San Joaquin Counties (Hoover 1937). Occurrences within the ECCC HCP/NCCP Inventory Area In the inventory area, big tarplant is known from 4 occurrences on Cowell Ranch, west of Brentwood, 7 occurrences on Roddy Ranch, south of Antioch, and one occurrence in Mount Diablo State Park, southeast of Clayton (California Natural Diversity Database 2005, Lake 2004). The historic occurrences in Antioch are likely to have been extirpated, although at least 1 population is present at Black Diamond Mines Regional Park (Preston pers. -
Northern Coastal Scrub and Coastal Prairie
GRBQ203-2845G-C07[180-207].qxd 12/02/2007 05:01 PM Page 180 Techbooks[PPG-Quark] SEVEN Northern Coastal Scrub and Coastal Prairie LAWRENCE D. FORD AND GREY F. HAYES INTRODUCTION prairies, as shrubs invade grasslands in the absence of graz- ing and fire. Because of the rarity of these habitats, we are NORTHERN COASTAL SCRUB seeing increasing recognition and regulation of them and of Classification and Locations the numerous sensitive species reliant on their resources. Northern Coastal Bluff Scrub In this chapter, we describe historic and current views on California Sagebrush Scrub habitat classification and ecological dynamics of these ecosys- Coyote Brush Scrub tems. As California’s vegetation ecologists shift to a more Other Scrub Types quantitative system of nomenclature, we suggest how the Composition many different associations of dominant species that make up Landscape Dynamics each of these systems relate to older classifications. We also Paleohistoric and Historic Landscapes propose a geographical distribution of northern coastal scrub Modern Landscapes and coastal prairie, and present information about their pale- Fire Ecology ohistoric origins and landscapes. A central concern for describ- Grazers ing and understanding these ecosystems is to inform better Succession stewardship and conservation. And so, we offer some conclu- sions about the current priorities for conservation, informa- COASTAL PRAIRIE tion about restoration, and suggestions for future research. Classification and Locations California Annual Grassland Northern Coastal Scrub California Oatgrass Moist Native Perennial Grassland Classification and Locations Endemics, Near-Endemics, and Species of Concern Conservation and Restoration Issues Among the many California shrub vegetation types, “coastal scrub” is appreciated for its delightful fragrances AREAS FOR FUTURE RESEARCH and intricate blooms that characterize the coastal experi- ence. -
Tarweed &Hellip
was apparent on both Cal 7 and DSL by mid-season of 1960. But Cal 7 gave a Tarweed higher lint yield than A4-42 and the DSL yield was below that of A4-42. The 1961 planting was made on a field where an a nuisance plant on California ranges observational block of DSL was grown in 1960. Following the wilted cotton of 1960, it was easy to detect wilt symptoms S. S. WINANS ’ C. M. MCKELL in mid-summer throughout the Ca17 and DSL plots, and minor symptoms were evi- dent even in A4-42 plots. Yields from this forms dense patches among and above location were considerably lower for all the dry annual forage species-obscuring varieties in 1961 than in 1960. Never- and limiting use of desirable species as theless, the grower allowed the test to dry feed by livestock. remain on the same plots in 1962. Some observations of tarweed seed However, the grower did switch the production, germination, and hard seed planting scheme from “solid” cotton to percentage were made to help show how “2-in, 2-out.” Significant yield differ- tarweed persists even though a seed crop ences were obtained among the varieties might fail to mature. Clipping and fall in 1962. A442 was outstanding for its application of nitrogen were studied as wilt tolerance even though the low sum- possible means of minimizing tarweed mer temperatures in 1962 were ideal for stands during the seedling stage. the wilt organism to operate. Heavy wilt Three tarweed-infested rangeland areas damage was evident in the Ca17 plots and located in the Sierra Nevada foothills in lint yield was 19% lower than A4-42, as Sacramento, Tuolumne, and Madera shown in the graph. -
Phylogenies and Secondary Chemistry in Arnica (Asteraceae)
Digital Comprehensive Summaries of Uppsala Dissertations from the Faculty of Science and Technology 392 Phylogenies and Secondary Chemistry in Arnica (Asteraceae) CATARINA EKENÄS ACTA UNIVERSITATIS UPSALIENSIS ISSN 1651-6214 UPPSALA ISBN 978-91-554-7092-0 2008 urn:nbn:se:uu:diva-8459 !"# $ % !& '((" !()(( * * * + , - . , / , '((", + 0 1# 2, # , 34', 56 , , 70 46"84!855&86(4'8(, - 1# 2 . * 9 10-2 . * . # 9 , * * 1 ! " #! !$ 2 1 2 .8 # * * :# 77 1%&'(2 . !6 '3, + . .8 ) / , ; < * . * ** # , * * * , 09 * . # * * 33 * != , 0- # 9 * * 1, , * 2 . * , 0 * * * * * . * , $ * 0- * % # , # 8 * * * * * * $8> # . * * !' , * * . ** , ? . 0- , +,- # # 7-0 -0 :+' 9 +# $8> ./0) . ) 1 ) 2 * 3) ) .456(7 ) , @ / '((" 700 !=5!8='!& 70 46"84!855&86(4'8( ) ))) 8"&54 1 );; ,/,; A B ) ))) 8"&542 List of Papers This thesis is based on the following papers, which are referred to in the text by their Roman numerals: I Ekenäs, C., B. G. Baldwin, and K. Andreasen. 2007. A molecular phylogenetic -
Sticky Plant Traps Insects to Enhance Indirect Defence
Ecology Letters, (2012) doi: 10.1111/ele.12032 LETTER Sticky plant traps insects to enhance indirect defence Abstract B. A. Krimmel1* and I. S. Pearse2 Plant-provided foods for predatory arthropods such as extrafloral nectar and protein bodies provide indi- rect plant defence by attracting natural enemies of herbivores, enhancing top-down control. Recently, ecol- ogists have also recognised the importance of carrion as a food source for predators. Sticky plants are widespread and often entrap and kill small insects, which we hypothesised would increase predator densi- ties and potentially affect indirect defence. We manipulated the abundance of this entrapped insect carrion on tarweed (Asteraceae: Madia elegans) plants under natural field conditions, and found that carrion augmen- tation increased the abundance of a suite of predators, decreased herbivory and increased plant fitness. We suggest that entrapped insect carrion may function broadly as a plant-provided food for predators on sticky plants. Keywords Enemy free space, glandular trichomes, indirect defense, omnivory, scavenging. Ecology Letters (2012) INTRODUCTION MATERIALS AND METHODS Extensive research has characterised the types of plant-provided We experimentally augmented carrion on tarweed (Asteraceae: Madia foods used by predators (W€ackers et al. 2005) such as pollen (Salas- elegans), an annual plant native to CA and OR. We then measured Aguilar & Ehler 1977; Wheeler 2001), extrafloral nectar (Janzen the responses of (1) predator abundance and diversity, (2) herbivore 1966; Bentley 1977; Heil et al. 2001) and protein bodies (Janzen damage and (3) plant lifetime fitness. At our study site, tarweed’s 1966). In addition to these non-prey food sources, carrion has major herbivore is the specialist caterpillar Heliothodes diminutiva recently been proposed as a ubiquitous and important resource for (Grote), which feeds largely on plant reproductive organs (Fig. -
Ukiah Western Hills Open Land Acquisition & Limited Development
Ukiah Western Hills Open Land Acquisition & Limited Development Agreement Draft Initial Study & Mitigated Negative Declaration Attachments April 16, 2021 ATTACHMENT A Existing Site Photographs Existing access road Existing water tank site Existing "house site" on one of the proposed Development Parcels ATTACHMENT B Prepared For: Michelle Irace, Planning Manager Department of Community Development 300 Seminary Avenue, Ukiah, CA 95482 APNs: 001-040-83, 157- 070-01, 157-070-02, and 003-190-01 Prepared by Jacobszoon & Associates, Inc. Alicia Ives Ringstad Senior Wildlife Biologist [email protected] Date: March 11, 2021 Updated: April 8, 2021 Biological Assessment Report Table of Contents Section 1.0: Introduction .................................................................................................................................................................. 2 Section 2.0: Regulations and Descriptions ....................................................................................................................................... 2 2.1 Regulatory Setting ................................................................................................................................................................. 2 2.2 Natural Communities and Sensitive Natural Communities .................................................................................................... 3 2.3 Special-Status Species...........................................................................................................................................................