Food Habits of Rodents Inhabiting Arid and Semi-Arid Ecosystems of Central New Mexico." (2007)

Total Page:16

File Type:pdf, Size:1020Kb

Food Habits of Rodents Inhabiting Arid and Semi-Arid Ecosystems of Central New Mexico. University of New Mexico UNM Digital Repository Special Publications Museum of Southwestern Biology 5-10-2007 Food Habits of Rodents Inhabiting Arid and Semi- arid Ecosystems of Central New Mexico Andrew G. Hope Robert R. Parmenter Follow this and additional works at: https://digitalrepository.unm.edu/msb_special_publications Recommended Citation Hope, Andrew G. and Robert R. Parmenter. "Food Habits of Rodents Inhabiting Arid and Semi-arid Ecosystems of Central New Mexico." (2007). https://digitalrepository.unm.edu/msb_special_publications/2 This Article is brought to you for free and open access by the Museum of Southwestern Biology at UNM Digital Repository. It has been accepted for inclusion in Special Publications by an authorized administrator of UNM Digital Repository. For more information, please contact [email protected]. SPECIAL PUBLICATION OF THE MUSEUM OF SOUTHWESTERN BIOLOGY NUMBER 9, pp. 1–75 10 May 2007 Food Habits of Rodents Inhabiting Arid and Semi-arid Ecosystems of Central New Mexico ANDREW G. HOPE AND ROBERT R. PARMENTER1 Special Publication of the Museum of Southwestern Biology 1 CONTENTS Abstract................................................................................................................................................ 5 Introduction ......................................................................................................................................... 5 Study Sites ........................................................................................................................................... 6 Cottonwood Riparian Forest ....................................................................................................... 6 Piñon-Juniper Woodland ............................................................................................................ 6 Juniper-Oak Savanna.................................................................................................................. 7 Mesquite Savanna ....................................................................................................................... 7 Short-Grass Steppe .................................................................................................................... 8 Chihuahuan Desert Scrubland .................................................................................................... 9 Methods ............................................................................................................................................... 9 Field Sampling ............................................................................................................................. 9 Diet Analyses ............................................................................................................................... 9 Data Analysis ............................................................................................................................. 10 Species Accounts of Diet Composition ............................................................................................ 10 Family Sciuridae: Spermophilus spilosoma (Spotted Ground Squirrel) ................................................................ 10 Family Heteromyidae: Perognathus flavescens (Plains Pocket Mouse) ................................................................... 13 Perognathus flavus (Silky Pocket Mouse) ........................................................................... 15 Dipodomys merriami (Merriam’s Kangaroo Rat) ............................................................... 18 Dipodomys ordii (Ord’s Kangaroo Rat) .............................................................................. 24 Dipodomys spectabilis (Banner-tailed Kangaroo Rat) ......................................................... 28 Family Muridae: Reithrodontomys megalotis (Western Harvest Mouse) ....................................................... 30 Peromyscus boylii (Brush Mouse) ....................................................................................... 32 Peromyscus eremicus (Cactus Mouse) .................................................................................. 33 Peromyscus leucopus (White-footed Mouse) ....................................................................... 34 Peromyscus truei (Piñon Mouse) ........................................................................................ 37 Onychomys arenicola (Mearn’s Grasshopper Mouse).......................................................... 39 Onychomys leucogaster (Northern Grasshopper Mouse) ..................................................... 40 Neotoma albigula (White-throated Woodrat).................................................................... 43 Neotoma micropus (Southern Plains Woodrat) ................................................................... 47 Diets of Rodents: Community Analyses ........................................................................................... 48 Comparisons Among Species of Rodents ................................................................................. 48 Comparisons Among Communities of Plants .......................................................................... 48 Plant Seeds as Food Resources for Rodents .............................................................................. 53 Acknowledgements............................................................................................................................ 58 Literature Cited ................................................................................................................................. 59 Appendix 1. Nomenclature for plants referenced in text ................................................................. 64 2 Food Habits of Rodents Inhabiting Arid and Semi-arid Ecosystems of Central New Mexico ◆ A.G. Hope, R.R.Parmenter LIST OF TABLES TABLE 1. List of rodents sampled on the Sevilleta National Wildlife Refuge, New Mexico. ....... 11 TABLE 2. List of items discovered in the diet of the plains pocket mouse (Perognathus flavescens) on the Sevilleta National Wildlife Refuge, New Mexico. ................................................................. 14 TABLE 3. Summary of prey types of the plains pocket mouse (Perognathus flavescens) on the Sevilleta National Wildlife Refuge, New Mexico. ............................................................................ 15 TABLE 4. List of items discovered in the diet of the silky pocket mouse (Perognathus flavus) on the Sevilleta National Wildlife Refuge, New Mexico. ............................................................................. 16 TABLE 5. Summary of prey types of the silky pocket mouse (Perognathus flavus) on the Sevilleta National Wildlife Refuge, New Mexico. ............................................................................. 17 TABLE 6. List of items discovered in the diet of Merriam’s kangaroo rat (Dipodomys merriami) on the Sevilleta National Wildlife Refuge, New Mexico. ................................................................. 19 TABLE 7. Summary of prey types of the Merriam’s kangaroo rat (Dipodomys merriami) on the Sevilleta National Wildlife Refuge, New Mexico. ................................................................. 20 TABLE 8. List of items discovered in the diet of Ord’s kangaroo rat (Dipodomys ordii) on the Sevilleta National Wildlife Refuge, New Mexico. ............................................................................. 25 TABLE 9. Summary of prey types of the Ord’s kangaroo rat (Dipodomys ordii) on the Sevilleta National Wildlife Refuge, New Mexico. ........................................................................................... 26 TABLE 10. List of items discovered in the diet of the western harvest mouse (Reithrodontomys megalotis) on the Sevilleta National Wildlife Refuge, New Mexico. ................................................. 31 TABLE 11. Summary of prey types of the western harvest mouse (Reithrodontomys megalotis) on the Sevilleta National Wildlife Refuge, New Mexico. ................................................................. 31 TABLE 12. List of items discovered in the diet of the brush mouse (Peromyscus boylii) on the Sevilleta National Wildlife Refuge, New Mexico. ............................................................................. 32 TABLE 13. Summary of prey types of the brush mouse (Peromyscus boylii) on the Sevilleta National Wildlife Refuge, New Mexico. ........................................................................................ 33 TABLE 14. List of items discovered in the diet of the white-footed mouse (Peromyscus leucopus) on the Sevilleta National Wildlife Refuge, New Mexico. ................................................................. 34 TABLE 15. Summary of prey types of the white-footed mouse (Peromyscus leucopus) on the Sevilleta National Wildlife Refuge, New Mexico. ............................................................................. 36 TABLE 16. List of items discovered in the diet of the piñon mouse (Peromyscus truei) on the Sevilleta National Wildlife Refuge, New Mexico. .............................................................................. 37 ...continued Special Publication of the Museum of Southwestern Biology 3 LIST OF TABLES, continued TABLE 17. Summary of prey types of the piñon mouse (Peromyscus truei) on the Sevilleta National Wildlife Refuge, New Mexico. .......................................................................................
Recommended publications
  • Mapping Prosopis Glandulosa (Mesquite) Invasion in the Arid Environment of South Africa Using Remote Sensing Techniques
    Mapping Prosopis glandulosa (mesquite) invasion in the arid environment of South Africa using remote sensing techniques NYASHA FLORENCE MURERIWA 0604748V Supervisor: Dr Elhadi Adam A dissertation submitted to the School of Geography, Archaeology and Environmental Studies, Faculty of Science, University of the Witwatersrand in fulfilment of the academic requirements for the degree of Master of Science in Environmental Sciences March 2016 Johannesburg South Africa Abstract Decades after the first introduction of the Prosopis spp. (mesquite) to South Africa in the late 1800s for its benefits, the invasive nature of the species became apparent as its spread in regions of South Africa resulting in devastating effects to biodiversity, ecosystems and the socio- economic wellbeing of affected regions. Various control and management practices that include biological, physical, chemical and integrated methods have been tested with minimal success as compared to the rapid spread of the species. From previous studies, it has been noted that one of the reasons for the low success rates in mesquite control and management is a lack of sufficient information on the species invasion dynamic in relation to its very similar co-existing species. In order to bridge this gap in knowledge, vegetation species mapping techniques that use remote sensing methods need to be tested for the monitoring, detection and mapping of the species spread. Unlike traditional field survey methods, remote sensing techniques are better at monitoring vegetation as they can cover very large areas and are time-effective and cost- effective. Thus, the aim of this research was to examine the possibility of mapping and spectrally discriminating Prosopis glandulosa from its native co-existing species in semi-arid parts of South Africa using remote sensing methods.
    [Show full text]
  • Taxonomic Revision of Genus Prosopis L. in Egypt
    International Journal of Environment Volume : 04 | Issue : 01 | Jan-Mar. | 2015 ISSN: 2077-4508 Pages: 13-20 Taxonomic revision of genus Prosopis L. in Egypt Abd El Halim A. Mohamed and Safwat A. Azer Flora and Phytotaxonomy Researches Department, Horticultural Research Institute, Agricultural Research Center, Dokki, Giza, Egypt ABSTRACT The aim of this work was to survey the new record invasive alien Prosopis juliflora and clarifies the taxonomic relationships among genus Prosopis L. in Egypt. The wild species are Prosopis farcta (Banks & Sol.) Macbride and Prosopis juliflora (Sw.) DC. The cultivated species are Prosopis cineraria (L.) Druce; Prosopis glandulosa Torr. and Prosopis strombulifera (Lam.) Benth. Based on morphological traits, the numerical analysis divided the Prosopis species into three clusters. Cluster one included: Prosopis glandulosa and Prosopis juliflora. Cluster two included: Prosopis farcta and Prosopis cineraria. Cluster three included: Prosopis strombulifera. According to the degree of similarity, the species of cluster one had the highest ratio (75%) followed by (55.6%) between the species of cluster two. Moreover, the highest ratio (33.3%) was recorded between Prosopis strombulifera and Prosopis juliflora, while the lowest ratio (20.8%) was recorded between Prosopis strombulifera and Prosopis cineraria. This work recoded Prosopis juliflora to the Flora of Egypt. Key words: Taxonomy, Prosopis, alien species, numerical analysis, similarity level, Egypt. Introduction The genus Prosopis L. belongs to the family Leguminosae, subfamily Mimosoideae, tribe Mimosae (Burkart, 1976; Sherry et al., 2011). It comprises 44 species and five sections based on observed morphological differences among studied taxa (Burkart, 1976). The five sections included: Prosopis; Anonychium; Strombocarpa; Monilicarpa and Algarobia (Burkart, 1976; Landeras et al., 2004; Elmeer and Almalki, 2011).
    [Show full text]
  • Mesquite Or Algarrobo
    Screening Prosopis (Mesquite or Algarrobo) Abstract: Eighty collections of Prosopis have been screened in field experiments for biomass for Biofuel Production on Semiarid Lands1 production, frost tolerance, and heat/drought tol- erance. Selections have been examined in the greenhouse for nitrogen fixation and salinity tolerance in which one species grew on a nitrogen Peter Felker, Peter R. Clark, G. H. Cannell, and Joseph F. free media in salinities equivalent to seawater. Osborn2 A 44 percent sugar pod producer was identified and successfully fermented to ethanol by Avgeri- nos and Wang at MIT. Individual trees have grown 5 to 7 cm in basal diameter and 2 to 3.2 meters in height per year with 600 mm total water applica- tion. Dry matter production of 14,000 kg/ha has been obtained at projected harvested costs of $23.00 per ton or $1.35 per million Btu and com- pare favorably with natural gas, heating oil, and coal at $3.0, and $6.0, and $1.50 per million Btu's respectively. In many regions of the world, wood is an en- In the screening of new plants for biofuel ergy source that is locally available, decentral- production it is important not to rule out a ized, and requires little capital expenditure for particular natural ecosystem because of low pro- either acquisition or conversion to useful forms ductivity since the biomass productivity of nat- of energy. In the last 5-8 years these character- ural stands provides little insight into produc- istics have led wood to overtake nuclear energy as tivity possible for managed food or fuel produc- an energy source for the United States without tion systems.
    [Show full text]
  • 31295015064529.Pdf (3.477Mb)
    POPULATION DYNAMICS, REPRODUCTION, AND ACTIVITIES OF THE KANGAROO RAT, DIPODOMYS ORDII, IN WESTERN TEXAS by HERSCHEL VJHITAKER GARNER, B.S., M.S. A DISSERTATION IN ZOOLOGY Submitted to the Graduate Faculty of Texas Tech University in Partial Fulfillment of the Requirements for the Degree of DOCTOR OF PHILOSOPHY Approved Accepted August, 1970 ACKNOWL EDGMENTS I am especially grateful to Professor Robert L. Packard for advising in research methods, aiding in collecting data, and critically reading the manuscript. Additional appreciated suggestions were made by Professors Archie C. Allen, John S. Mecham, Robert W.. Mitchell, Paul V. Prior (now at the University of Nebraska- Omaha), and Chester M. Rowell. Mr. Robert B. Wadley pro­ vided useful help in developing computer programs used in sorting and analysis of the data. An honorarium from the Department of Biology defrayed some of the cost of travel to the field. My wife, Anita, aided in making collections and recording data. Additional thanks are extended to fellow graduate students who provided help and ideas.' 11 TABLE OF CONTENTS ACKNOWLEDGMENTS ii LIST OF TABLES ; . iv LIST OF ILLUSTRATIONS V I. INTRODUCTION 1 II. METHODS AND MATERIALS 3 III. REPRODUCTION 15 IV. ACTIVITIES 35 V. POPULATION DYNAMICS 43 VI. SUMlvlARY AND CONCLUSIONS 72 LITERATURE CITED 76 111 LIST OF TABLES Table Page 1. Estimation of number of D. ordii on the Kermit area 51 IV LIST OF ILLUSTRATIONS Figure Page 1. The intensive study area viewed from the southern periphery June, 1956 .... 5 2. Diagram of study area showing position of activity center values of animals used in the experimental activity studies 12 3.
    [Show full text]
  • Final Report: Lesser Prairie-Chicken Survey − Kiowa and Rita Blanca National Grasslands, 2014
    Final Report: Lesser Prairie-Chicken Survey − Kiowa and Rita Blanca National Grasslands, 2014 Project Manager: Angela Dwyer, Rocky Mountain Bird Observatory, 230 Cherry St., Fort Collins, CO 80521 ([email protected]) Project Director: David Hanni, Rocky Mountain Bird Observatory, 230 Cherry St., Fort Collins, CO 80521 ([email protected]) Introduction The Lesser Prairie-Chicken (Tympanuchus pallidicinctus) (LEPC) occupies grassland habitat consisting of sand sagebrush (Artemisia filifolia), sand shinnery oak (Quercus havardii) and mixed grass vegetation communities of the southern Great Plains. Since the 19th century, LEPC and the habitat upon which they depend has diminished across their historical range (Crawford and Bolen 1976, Taylor and Guthery 1980a), with recent estimates of current occupied range totaling approximately 17% of the estimated area of their historical range. Causes for this reduction in occupied range are primarily attributed to habitat loss and fragmentation (USFWS 2012). Habitat loss has been caused by conversion of native prairie to cropland (Bent 1932, Copelin 1963, Taylor and Guthery 1980) and long term fire suppression (Woodward et al. 2001) leading to tree invasion (Fuhlendorf et al. 2002). Grazing management practices would help improve habitat if managed to benefit LEPC. Heavily grazed fields that leave no residual vegetation for broods can be detrimental to LEPC (Sell 1979, Hunt and Best 2010). Habitat fragmentation has resulted from a combination of habitat loss and degradation caused by oil and gas development (Hunt 2004) and suspected effects of wind energy development (Pruett et al. 2009). The LEPC is not thought to occur in Kiowa and Rita Blanca National Grasslands (KRB) (Giesen 2003), however some parcels within the grasslands are managed for LEPC.
    [Show full text]
  • Response of Selected Plants to Fire on White Sands
    Session D—Ecology of Fire on White Sands Missile Range—Boykin Response of Selected Plants to Fire on 1 White Sands Missile Range, New Mexico 2 Kenneth G. Boykin Abstract Little was known about the ecology, impacts, effects, and history of fire related to many plants and communities within White Sands Missile Range. I began by identifying the known aspects and the gaps in knowledge for White Sands Missile Range. I analyzed existing data available for the Installation taken from the Integrated Training and Area Management (ITAM) program for 1988 to 1999. Burn plots were identified at 34 sites with fires occurring sometime within that 11 yr span. Selected plant species were analyzed to identify the response to fire including change in frequency, cover, and structure. Analysis of data indicated varied responses to fire and identified a need for long term monitoring to account for natural variability. Introduction Fire is a major factor influencing the ecology, evolution, and biogeography of many vegetation communities (Humphrey 1974, Ford and McPherson 1996). In the Southwest, semi-desert grasslands and shrublands have evolved with fires caused by lightning strikes (Pyne 1982, Betancourt and others 1990). Fires have maintained grasslands by reducing invading shrubs (Valentine 1971). The impact these fires have on the ecosystem depends not only on current biological and physical environment but also on past land use patterns (Ford and McPherson 1996). Fires impact communities by affecting species diversity, persistence, opportunistic invading species, insects, diseases, and herbivores. Plant species diversity often increases after fires and some communities are dependent on fire to maintain their structure (Jacoby 1998).
    [Show full text]
  • A Vegetation Map of Carlsbad Caverns National Park, New Mexico 1
    ______________________________________________________________________________ A Vegetation Map of Carlsbad Caverns National Park, New Mexico ______________________________________________________________________________ 2003 A Vegetation Map of Carlsbad Caverns National Park, New Mexico 1 Esteban Muldavin, Paul Neville, Paul Arbetan, Yvonne Chauvin, Amanda Browder, and Teri Neville2 ABSTRACT A vegetation classification and high resolution vegetation map was developed for Carlsbad Caverns National Park, New Mexico to support natural resources management, particularly fire management and rare species habitat analysis. The classification and map were based on 400 field plots collected between 1999 and 2002. The vegetation communities of Carlsbad Caverns NP are diverse. They range from desert shrublands and semi-grasslands of the lowland basins and foothills up through montane grasslands, shrublands, and woodlands of the highest elevations. Using various multivariate statistical tools, we identified 85 plant associations for the park, many of them unique in the Southwest. The vegetation map was developed using a combination of automated digital processing (supervised classifications) and direct image interpretation of high-resolution satellite imagery (Landsat Thematic Mapper and IKONOS). The map is composed of 34 map units derived from the vegetation classification, and is designed to facilitate ecologically based natural resources management at a 1:24,000 scale with 0.5 ha minimum map unit size (NPS national standard). Along with an overview of the vegetation ecology of the park in the context of the classification, descriptions of the composition and distribution of each map unit are provided. The map was delivered both in hard copy and in digital form as part of a geographic information system (GIS) compatible with that used in the park.
    [Show full text]
  • GOOSEBERRYLEAF GLOBEMALLOW Sphaeralcea Grossulariifolia (Hook
    GOOSEBERRYLEAF GLOBEMALLOW Sphaeralcea grossulariifolia (Hook. & Arn.) Rydb. Malvaceae – Mallow family Corey L. Gucker & Nancy L. Shaw | 2018 ORGANIZATION NOMENCLATURE Sphaeralcea grossulariifolia (Hook. & Arn.) Names, subtaxa, chromosome number(s), hybridization. Rydb., hereafter referred to as gooseberryleaf globemallow, belongs to the Malveae tribe of the Malvaceae or mallow family (Kearney 1935; La Duke 2016). Range, habitat, plant associations, elevation, soils. NRCS Plant Code. SPGR2 (USDA NRCS 2017). Subtaxa. The Flora of North America (La Duke 2016) does not recognize any varieties or Life form, morphology, distinguishing characteristics, reproduction. subspecies. Synonyms. Malvastrum coccineum (Nuttall) A. Gray var. grossulariifolium (Hooker & Arnott) Growth rate, successional status, disturbance ecology, importance to animals/people. Torrey, M. grossulariifolium (Hooker & Arnott) A. Gray, Sida grossulariifolia Hooker & Arnott, Sphaeralcea grossulariifolia subsp. pedata Current or potential uses in restoration. (Torrey ex A. Gray) Kearney, S. grossulariifolia var. pedata (Torrey ex A. Gray) Kearney, S. pedata Torrey ex A. Gray (La Duke 2016). Seed sourcing, wildland seed collection, seed cleaning, storage, Common Names. Gooseberryleaf globemallow, testing and marketing standards. current-leaf globemallow (La Duke 2016). Chromosome Number. Chromosome number is stable, 2n = 20, and plants are diploid (La Duke Recommendations/guidelines for producing seed. 2016). Hybridization. Hybridization occurs within the Sphaeralcea genus.
    [Show full text]
  • Germination and Seedling Establishment of Spiny Hopsage (Grayia Spinosa [Hook.] Moq.)
    AN ABSTRACT OF THE THESIS OF Nancy L. Shaw for the degree of Doctor of Philosophy in Crop and Soil Sciences presented on March 19, 1992 Title: Germination and Seedling Establishment of Spiny Hopsage (Grayia Spinosa [Hook.] Moq.) Abstract approved:_Redactedfor Privacy von r. ULdUe Reestablishment of spiny hopsage(Grayia spinosa [Hook.] Moq.) where depleted or lost on shrub steppe sites can improve forage, plant cover, and soil stabilization. The objectives of this study were to: 1) determine direct-seeding requirements; 2) develop optimum germination pretreatments; and 3) examine dormancy mechanisms in spiny hopsage fruits and seeds. The effects of seed source, planting date,and site preparation method onseed germination and seedling establishment (SE) were examined at Birds of Prey and Reynolds Creek in southwestern Idaho. Three seed sources were planted on rough or compact seedbeds on 4 dates in 1986-87 and 3 dates in 1987-88. Exposure to cool-moist environments improved spring SE from early fall (EF) and late fall (LF) plantings. Few seedlings emerged from early (ESp) or late spring (LSp) plantings. SE was low at: 1 site in 1986-87 and atboth sites in 1987-88, probably due to lack of precipitation. For the successful 1986-87 planting, seedling density was greater on rough compared to compact seedbeds in April andMay, possiblydue to improved microclimate conditions. Growth rate varied among seed sources, but seedlings developed a deep taproot (mean length 266 mm) with few lateral roots the first season. Seeds were planted on 3 dates in 1986-87 and 1987-88, andnylon bags containing seeds were planted on 4 dates each year to study microenvironment effects on germination (G), germination rate (GR), and SE.
    [Show full text]
  • Ajo Peak to Tinajas Altas: a Flora of Southwestern Arizona
    Felger, R.S., S. Rutman, and J. Malusa. 2014. Ajo Peak to Tinajas Altas: A flora of southwestern Arizona. Part 6. Poaceae – grass family. Phytoneuron 2014-35: 1–139. Published 17 March 2014. ISSN 2153 733X AJO PEAK TO TINAJAS ALTAS: A FLORA OF SOUTHWESTERN ARIZONA Part 6. POACEAE – GRASS FAMILY RICHARD STEPHEN FELGER Herbarium, University of Arizona Tucson, Arizona 85721 & Sky Island Alliance P.O. Box 41165, Tucson, Arizona 85717 *Author for correspondence: [email protected] SUSAN RUTMAN 90 West 10th Street Ajo, Arizona 85321 JIM MALUSA School of Natural Resources and the Environment University of Arizona Tucson, Arizona 85721 [email protected] ABSTRACT A floristic account is provided for the grass family as part of the vascular plant flora of the contiguous protected areas of Organ Pipe Cactus National Monument, Cabeza Prieta National Wildlife Refuge, and the Tinajas Altas Region in southwestern Arizona. This is the second largest family in the flora area after Asteraceae. A total of 97 taxa in 46 genera of grasses are included in this publication, which includes ones established and reproducing in the modern flora (86 taxa in 43 genera), some occurring at the margins of the flora area or no long known from the area, and ice age fossils. At least 28 taxa are known by fossils recovered from packrat middens, five of which have not been found in the modern flora: little barley ( Hordeum pusillum ), cliff muhly ( Muhlenbergia polycaulis ), Paspalum sp., mutton bluegrass ( Poa fendleriana ), and bulb panic grass ( Zuloagaea bulbosa ). Non-native grasses are represented by 27 species, or 28% of the modern grass flora.
    [Show full text]
  • December 2012 Number 1
    Calochortiana December 2012 Number 1 December 2012 Number 1 CONTENTS Proceedings of the Fifth South- western Rare and Endangered Plant Conference Calochortiana, a new publication of the Utah Native Plant Society . 3 The Fifth Southwestern Rare and En- dangered Plant Conference, Salt Lake City, Utah, March 2009 . 3 Abstracts of presentations and posters not submitted for the proceedings . 4 Southwestern cienegas: Rare habitats for endangered wetland plants. Robert Sivinski . 17 A new look at ranking plant rarity for conservation purposes, with an em- phasis on the flora of the American Southwest. John R. Spence . 25 The contribution of Cedar Breaks Na- tional Monument to the conservation of vascular plant diversity in Utah. Walter Fertig and Douglas N. Rey- nolds . 35 Studying the seed bank dynamics of rare plants. Susan Meyer . 46 East meets west: Rare desert Alliums in Arizona. John L. Anderson . 56 Calochortus nuttallii (Sego lily), Spatial patterns of endemic plant spe- state flower of Utah. By Kaye cies of the Colorado Plateau. Crystal Thorne. Krause . 63 Continued on page 2 Copyright 2012 Utah Native Plant Society. All Rights Reserved. Utah Native Plant Society Utah Native Plant Society, PO Box 520041, Salt Lake Copyright 2012 Utah Native Plant Society. All Rights City, Utah, 84152-0041. www.unps.org Reserved. Calochortiana is a publication of the Utah Native Plant Society, a 501(c)(3) not-for-profit organi- Editor: Walter Fertig ([email protected]), zation dedicated to conserving and promoting steward- Editorial Committee: Walter Fertig, Mindy Wheeler, ship of our native plants. Leila Shultz, and Susan Meyer CONTENTS, continued Biogeography of rare plants of the Ash Meadows National Wildlife Refuge, Nevada.
    [Show full text]
  • A Reciprocal Transplant Experiment with Winterfat (Krascheninnikovia Lanata) Melanie Barnes
    University of New Mexico UNM Digital Repository Biology ETDs Electronic Theses and Dissertations 12-1-2009 The effect of plant source location on restoration success: a reciprocal transplant experiment with winterfat (Krascheninnikovia lanata) Melanie Barnes Follow this and additional works at: https://digitalrepository.unm.edu/biol_etds Recommended Citation Barnes, Melanie. "The effect of plant source location on restoration success: a reciprocal transplant experiment with winterfat (Krascheninnikovia lanata)." (2009). https://digitalrepository.unm.edu/biol_etds/4 This Dissertation is brought to you for free and open access by the Electronic Theses and Dissertations at UNM Digital Repository. It has been accepted for inclusion in Biology ETDs by an authorized administrator of UNM Digital Repository. For more information, please contact [email protected]. The effect of plant source location on restoration success: a reciprocal transplant experiment with winterfat (Krascheninnikovia lanata) BY Melanie G. Barnes B.A., Biology, Reed College, 2001 DISSERTATION Submitted in Partial Fulfillment of the Requirements for the Degree of Doctor of Philosophy Biology The University of New Mexico Albuquerque, New Mexico December, 2009 DEDICATION In memory of my mother, Georgene Grace Barnes. The completion of this dissertation is also dedicated to my friends and family who have supported me in this endeavor and who taught me many things about life that gave me the perspective I needed to complete this work. I would like to thank Heather Simpson, Jerusha Reynolds, Terri Koontz, Nathan Abrahamson, Jeremy Barlow, Brittany Barker, Laura Calabrese, Jennifer Hollis, Maureen Peters, Helen Barnes, and Tom Barnes. Finally, I want to thank Lisa for her love and emotional support; it means the world to me.
    [Show full text]