Accounting for Imperfect Detection Reveals Role of Host Traits in Structuring Viral Diversity

Total Page:16

File Type:pdf, Size:1020Kb

Accounting for Imperfect Detection Reveals Role of Host Traits in Structuring Viral Diversity bioRxiv preprint doi: https://doi.org/10.1101/2020.06.29.178798; this version posted June 30, 2020. The copyright holder for this preprint (which was not certified by peer review) is the author/funder, who has granted bioRxiv a license to display the preprint in perpetuity. It is made available under aCC-BY-NC-ND 4.0 International license. 1 Accounting for imperfect detection reveals role of host traits in structuring viral diversity 2 of a wild bat community 3 4 Anna R. Sjodin1,2,*, Simon J. Anthony3, Michael R. Willig1,4, Morgan W. Tingley1,5 5 6 1 Ecology and Evolutionary Biology, University of Connecticut, 75 N. Eagleville Road, Unit 7 3043, Storrs, Connecticut, USA 06269 8 2 Biological Sciences, University of Idaho, 875 Perimeter Drive, MS 3051, Moscow, Idaho, USA 9 83844 10 3 Center for Infection and Immunity, Columbia University, 722 W. 168th Street, 17th Floor, New 11 York, New York, USA 10032 12 4 Center for Environmental Sciences & Engineering and Institute of the Environment, University 13 of Connecticut, Storrs, Connecticut, USA 06269 14 5 Ecology and Evolutionary Biology, University of California – Los Angeles, 621 Charles E 15 Young Drive South, Los Angeles, California, USA 90095 16 17 18 * Corresponding author 19 email: [email protected] 1 bioRxiv preprint doi: https://doi.org/10.1101/2020.06.29.178798; this version posted June 30, 2020. The copyright holder for this preprint (which was not certified by peer review) is the author/funder, who has granted bioRxiv a license to display the preprint in perpetuity. It is made available under aCC-BY-NC-ND 4.0 International license. 20 Abstract: Understanding how multi-scale host heterogeneity affects viral community assembly 21 can illuminate ecological drivers of infection and host-switching. Yet, such studies are hindered 22 by imperfect viral detection. To address this issue, we used a community occupancy model – 23 refashioned for the hierarchical nature of molecular-detection methods – to account for failed 24 detection when examining how individual-level host traits affect herpesvirus richness in eight 25 species of wild bats. We then used model predictions to examine the role of host sex and species 26 identity on viral diversity at the levels of host individual, population, and community. Results 27 demonstrate that cPCR and viral sequencing failed to perfectly detect viral presence. 28 Nevertheless, model estimates correcting for imperfect detection show that reproductively active 29 bats, especially reproductively active females, have significantly higher viral richness, and host 30 sex and species identity interact to affect viral richness. Further, host sex significantly affects 31 viral turnover across host populations, as females host more heterogeneous viral communities 32 than do males. Results suggest models of viral ecology benefit from integration of multi-scale 33 host factors, with implications for bat conservation and epidemiology. Furthermore, by 34 accounting for imperfect detection in laboratory assays, we demonstrate how statistical models 35 developed for other purposes hold promising possibilities for molecular and epidemiological 36 applications. 37 38 Key Words: 39 cPCR, Chiroptera, Herpesvirus, Occupancy Modeling, Virus Community 2 bioRxiv preprint doi: https://doi.org/10.1101/2020.06.29.178798; this version posted June 30, 2020. The copyright holder for this preprint (which was not certified by peer review) is the author/funder, who has granted bioRxiv a license to display the preprint in perpetuity. It is made available under aCC-BY-NC-ND 4.0 International license. 40 1. Introduction: 41 Emerging infectious viruses, such as SARS-CoV 2 or Zika, represent single pathogen 42 species embedded within multi-host, multi-pathogen systems. Community ecology – at the scale 43 of host communities, and also at the scale of viral communities – is increasingly recognized as a 44 productive framework with which to dissect such complex dynamics, illuminating risk factors 45 associated with pathogen transmission, host switching, and spillover from wildlife to humans, 46 among others [1, 2, 3, 4, 5, 6]. However, viral community ecology is limited by two major 47 quantitative obstacles. First, most viruses are rare [7, 8, 9, 10, 11]. This means that large numbers 48 of host individuals must be sampled for population-level detection, and resulting datasets are 49 highly zero-inflated. Second, many wildlife viruses remain unknown to science [12, 13]. 50 Currently, two of the most common methods for characterizing viral communities and 51 finding new viral taxa are unbiased high-throughput sequencing (HTS; e.g. metagenomics) and 52 consensus polymerase chain reaction (cPCR; [10]). HTS is advantageous when the goal is to 53 construct an entire viral genome or when so little is known about the target taxon that primers 54 cannot be designed. However, HTS lacks the sensitivity of PCR methods. cPCR is a method that 55 relies on the use of degenerate primers for the broad amplification of both known and unknown 56 viruses [10, 12]. It targets genome regions that are highly conserved among related viruses (e.g. 57 at the family or genus level) and can detect multiple coinfecting viruses, if present. The 58 degenerate primers bind with different efficiency to different viruses within a targeted taxon, so 59 viruses with lower homology in the primer-binding region will not be detected as efficiently as 60 would viruses with high sequence homology. Additionally, degenerate primers are, by definition, 61 less specific. This reduces the sensitivity of cPCR and increases the probability of false negatives 62 when viral load in the sample is low. This is a particular problem in wildlife surveys, where 3 bioRxiv preprint doi: https://doi.org/10.1101/2020.06.29.178798; this version posted June 30, 2020. The copyright holder for this preprint (which was not certified by peer review) is the author/funder, who has granted bioRxiv a license to display the preprint in perpetuity. It is made available under aCC-BY-NC-ND 4.0 International license. 63 many samples are taken from healthy or asymptomatic animals [4, 14, 15, 16, 17, 18], and 64 absence of symptoms is often associated with low viral load [19, 20, 21]. As a result, both HTS 65 and cPCR methods have a high possibility of failed detection of true infections (i.e. false 66 negatives). 67 Viral ecological studies using HTS and cPCR methods have mostly failed to account for 68 the issues of false negatives. In general, high rates of false negatives are acknowledged (e.g. [4, 69 22]) but are rarely considered a major problem preventing honest inference. This becomes 70 particularly problematic for studies of viral diversity and community assembly when accurate 71 measures of the number and identity of detected viruses are necessary to infer patterns and 72 mechanisms of co-infecting viruses. As consequent viral OTUs are missed for each sampled 73 individual, the missing data compound when individuals are aggregated at the population and 74 community levels. A handful of recent studies have used occupancy modeling techniques, 75 adapted from wildlife ecology (where sites are surveyed to detect species, rather than where 76 individual animals are assayed to detect viral strains), to better account for imperfect detection in 77 an epidemiological context [23, 24, 25, 26]. However, as best we are aware, no one has yet 78 adapted these methods to the detection process when using HTS or cPCR for biodiversity 79 discovery or characterization of viral community ecology [27], and it is not a common practice to 80 statistically account for failed detection in such a way across molecular biology more generally. 81 Additionally, viral ecologists have struggled to synthesize community dynamics across 82 host scales. For example, infection heterogeneity among individuals is a key element in 83 infectious disease dynamics [28, 29, 30] that is still relatively unexplored in viral communities of 84 wildlife. Pathogen aggregation in host individuals can affect pathogen interactions, transmission, 85 and host fitness, scaling up to alter population and community dynamics of the host. Failure to 4 bioRxiv preprint doi: https://doi.org/10.1101/2020.06.29.178798; this version posted June 30, 2020. The copyright holder for this preprint (which was not certified by peer review) is the author/funder, who has granted bioRxiv a license to display the preprint in perpetuity. It is made available under aCC-BY-NC-ND 4.0 International license. 86 account for such heterogeneity has potentially dangerous or expensive consequences for 87 modelling outbreak probabilities and forecasting disease spread [31, 32, 33]. 88 Bats are an important host to understand from the perspective of viral transmission, as 89 they seem to harbor a high number of viruses capable of infecting humans [34, 35, 36]. Cave- 90 roosting bats in Puerto Rico are abundant and relatively easily captured, making them a practical 91 system for addressing viral dynamics from an ecological perspective. Additionally, much is 92 known about their behavior, biology, and life history that can guide contextual understanding of 93 viral community dynamics [37]. For example, most cave-roosting species in Puerto Rico show 94 sex-related spatial segregation during reproduction [37]. Females often use a centralized 95 maternity colony within the cave, where they frequently and repeatedly come into contact with 96 the same individuals. Males do not use this space. By continually re-exposing themselves to the 97 same individual conspecifics, females likely reduce the variety of viruses to which they are 98 exposed. Thus, host sex likely effects pathogen diversity. Indeed, the role of host sex has shown 99 female-biased effects on ectoparasite and macro-parasite infection in Puerto Rican bats [38, 39]. 100 Furthermore, many Puerto Rican caves are well-studied in terms of bat diversity and abundance.
Recommended publications
  • Eastern Small-Footed Myotis (Myotis Leibii)
    ========================================================================== Current Status and Conservation Strategy for the Eastern Small-footed Myotis (Myotis leibii) October 2001 Technical Report #00-19 =========================================================================== Current Status and Conservation Strategy for the Eastern Small-footed Myotis (Myotis leibii) Prepared by: Sandra Y. Erdle and Christopher S. Hobson for: The George Washington and Jefferson National Forests Virginia Department of Conservation and Recreation Division of Natural Heritage 217 Governor Street Richmond, Virginia 23219 (804) 786-7951 Technical Report #00-19 This document may be cited as follows: Erdle, S. Y., and C. S. Hobson. 2001. Current status and conservation strategy for the eastern small-footed myotis (Myotis leibii). Natural Heritage Technical Report # 00-19. Virginia Department of Conservation and Recreation, Division of Natural Heritage, Richmond, VA. 17 pp + appendices. Virginia Department of Conservation and Recreation programs, activities, and employment opportunities are available to all people regardless of race, color, religion, sex, age, disability, national origin, or political affiliation. An equal opportunity/affirmative action employer. Current status and conservation strategy: Myotis leibii (October 2001) 2 CONTENTS ACKNOWLEDGMENTS . ii INTRODUCTION. 1 LIFE HISTORY AND ECOLOGY . 2 Taxonomy . 2 General Characteristics . 2 Distribution and Abundance . 2 Conservation Status . 4 Summer Ecology and Behavior . 4 Winter Ecology and Behavior . 5 Ecologic and Economic Importance . 5 Ontogeny and Reproduction . 6 Predators . 7 DISCUSSION AND MANAGEMENT RECOMMENDATIONS . 7 CONSERVATION AND PROTECTION . 9 Recommendations . 9 Information Needs . 10 PERTINENT LITERATURE . 12 APPENDICES . 18 Appendix A - Survey Form - List of Personal Contacts and Plan Reviewers - Responses to Survey Form Appendix B - Explanation of the Natural Heritage Ranking System Appendix C - Poster Abstract (American Society of Mammalogists) FIGURES Figure 1.
    [Show full text]
  • Spatial and Predictive Foraging Models for Gray Bats in Northwest Georgia and a Comparison of Two Acoustical Bat Survey Techniques
    Graduate Theses, Dissertations, and Problem Reports 2002 Spatial and predictive foraging models for gray bats in northwest Georgia and a comparison of two acoustical bat survey techniques Joshua Begg Johnson West Virginia University Follow this and additional works at: https://researchrepository.wvu.edu/etd Recommended Citation Johnson, Joshua Begg, "Spatial and predictive foraging models for gray bats in northwest Georgia and a comparison of two acoustical bat survey techniques" (2002). Graduate Theses, Dissertations, and Problem Reports. 1476. https://researchrepository.wvu.edu/etd/1476 This Thesis is protected by copyright and/or related rights. It has been brought to you by the The Research Repository @ WVU with permission from the rights-holder(s). You are free to use this Thesis in any way that is permitted by the copyright and related rights legislation that applies to your use. For other uses you must obtain permission from the rights-holder(s) directly, unless additional rights are indicated by a Creative Commons license in the record and/ or on the work itself. This Thesis has been accepted for inclusion in WVU Graduate Theses, Dissertations, and Problem Reports collection by an authorized administrator of The Research Repository @ WVU. For more information, please contact [email protected]. SPATIAL AND PREDICTIVE FORAGING MODELS FOR GRAY BATS IN NORTHWEST GEORGIA AND A COMPARISON OF TWO ACOUSTICAL BAT SURVEY TECHNIQUES Joshua B. Johnson Thesis submitted to the College of Agriculture, Forestry, and Consumer Sciences at West Virginia University in partial fulfillment of the requirements for the degree of Master of Science in Wildlife and Fisheries Resources W.
    [Show full text]
  • FWS 2009 Gray Bat
    Gray Bat (Myotis grisescens) 5-Year Review: Summary and Evaluation U.S. Fish and Wildlife Service Midwest Region Columbia, Missouri Ecological Services Field Office Columbia, Missouri 5-YEAR REVIEW Gray bat/Myotis grisescens 1.0 GENERAL INFORMATION 1.1 Reviewers U.S. Fish and Wildlife Service biologists in the offices listed below provided valuable additional information and corrections to a draft of this Review. Lead Regional Office: Carlita Payne, Midwest Regional Office; 612-713-5339 Lead Field Office: Paul McKenzie, Columbia, Missouri Ecological Services Field Office, MO; 573-234-2132, ext. 107 Cooperating Field Offices: Region 2: Richard Stark, Tulsa, Oklahoma Ecological Services Field Office, OK; 918-581-7458 Region 3: Jody Millar, Rock Island Ecological Services Field Office, IL; 309-575-5800, ext. 202; Andrew King, Bloomington Ecological Services Field Office, IN; 812-334-4261, ext. 216 Region 4: Lee Andrews, Kentucky Ecological Services Field Office, KY; 502-695-0468, ext. 108 Region 5: Tylan Dean, Gloucester, Virginia Field Office, VA; 804-693-6694, ext. 104 Region 6: Dan Mulhern, Manhattan Ecological Services Field Office, KS; 785-539-3474, ext. 109 Cooperating Regional Offices: Southwest Region: Wendy Brown; 505-248-6664 Southeast Region: Kelly Bibb; 404-679-7132 Northeast Region: Mary Parkin; 617-876-6173 Mountain-Prairie Region: Seth Willey; 303-236-4257 1.2 Methodology used to complete the review: The U.S. Fish and Wildlife Service’s (USFWS) Columbia, Missouri Ecological Services Field Office (Columbia, Missouri Field Office) completed this review. The March 30, 2006, Federal Register notice initiating this 5-year review (71 FR 16176), requested new scientific or commercial data and information that may have a bearing on the gray bat’s (Myotis grisescens) classification of endangered.
    [Show full text]
  • White-Nose Syndrome the Devastating Disease of Hibernating Bats in North America August 2012
    U.S. Fish & Wildlife Service White-nose syndrome The devastating disease of hibernating bats in North America August 2012 What is white-nose syndrome? White-nose syndrome is a disease affecting hibernating bats. Named for the white fungus that appears on the muzzle and other body parts of hibernating bats, WNS is associated with extensive mortality of bats in eastern North America. First documented in New York in the winter of 2006-2007, WNS has spread rapidly across the eastern United States and Canada, and the fungus that causes WNS has been detected as far west as Oklahoma. Bats with WNS exhibit uncharacteristic behavior during cold winter months, including flying outside in the day Marvin Moriarty/USFWS and clustering near the entrances of Bat with white-nose syndrome hibernacula. Bats have been found sick Numerous laboratories and state and n Tricolored bat (Perimyotis and dying in unprecedented numbers federal biologists are investigating subflavus) in and around caves and mines. WNS the cause of the bat deaths. A has killed more than 5.5 million bats newly discovered fungus, Geomyces Bat species on which Geomyces in the Northeast and Canada. In some destructans, has been demonstrated to destructans has been detected: hibernacula, 90 to 100 percent of bats cause WNS. Scientists are investigating n Cave bat (Myotis velifer) have died. the dynamics of fungal infection and n Southeastern bat (Myotis transmission, and searching for a way austroriparius) to control it. Federally listed species found in What bats are being affected? the affected area that have not yet More than half of the 45 bat species been confirmed with WNS or fungal living in the United States rely on infection: hibernation for winter survival.
    [Show full text]
  • Indiana Bat Habitat Requirements
    Section II-F Bat Habitat Conservation Priorities in Missouri Indiana Bat, Northern Long-Eared Bat, and Gray Bat NOTE: The Missouri Heritage Database, adapted for NRCS Field Office Technical Guide use, will be consulted for potential impacts to the Indiana Bat, Northern Long- Eared Bat, and Gray Bat. Please refer questions regarding these Bat Habitat Conservation Priorities to the Area Biologist. Area staff should direct questions to the State Wildlife Biologist. Indiana Bat The Indiana Bat (Myotis sodalis) is a federal and state listed endangered species. When the Natural Resources Conservation Service (NRCS) provides technical or financial assistance to landowners, habitat for this species must be considered and evaluated by NRCS staff that has completed the joint agency workshop, “U. S. Fish and Wildlife Service/NRCS Coordination for the Conservation of the Indiana Bat in Missouri.” Biology of the Indiana Bat From late fall through winter, Indiana bats in Missouri hibernate in caves in the Ozark Region. During the spring and summer, the bats utilize living, injured (e.g. split trunks and broken limbs from lightening strikes or wind), dead or dying trees for roosting throughout the state. Indiana bat roost trees tend to be greater than 9 inches (dbh) with loose or exfoliating bark. Large trees (greater than 20 inches dbh) are preferred. Most important are the structural characteristics that provide adequate space for bats to roost. Preferred roost sites are located in forest openings, at the forest edge, or where the overstory canopy allows some sunlight exposure to the roost tree which is usually within 0.6 miles of water.
    [Show full text]
  • Index of Handbook of the Mammals of the World. Vol. 9. Bats
    Index of Handbook of the Mammals of the World. Vol. 9. Bats A agnella, Kerivoula 901 Anchieta’s Bat 814 aquilus, Glischropus 763 Aba Leaf-nosed Bat 247 aladdin, Pipistrellus pipistrellus 771 Anchieta’s Broad-faced Fruit Bat 94 aquilus, Platyrrhinus 567 Aba Roundleaf Bat 247 alascensis, Myotis lucifugus 927 Anchieta’s Pipistrelle 814 Arabian Barbastelle 861 abae, Hipposideros 247 alaschanicus, Hypsugo 810 anchietae, Plerotes 94 Arabian Horseshoe Bat 296 abae, Rhinolophus fumigatus 290 Alashanian Pipistrelle 810 ancricola, Myotis 957 Arabian Mouse-tailed Bat 164, 170, 176 abbotti, Myotis hasseltii 970 alba, Ectophylla 466, 480, 569 Andaman Horseshoe Bat 314 Arabian Pipistrelle 810 abditum, Megaderma spasma 191 albatus, Myopterus daubentonii 663 Andaman Intermediate Horseshoe Arabian Trident Bat 229 Abo Bat 725, 832 Alberico’s Broad-nosed Bat 565 Bat 321 Arabian Trident Leaf-nosed Bat 229 Abo Butterfly Bat 725, 832 albericoi, Platyrrhinus 565 andamanensis, Rhinolophus 321 arabica, Asellia 229 abramus, Pipistrellus 777 albescens, Myotis 940 Andean Fruit Bat 547 arabicus, Hypsugo 810 abrasus, Cynomops 604, 640 albicollis, Megaerops 64 Andersen’s Bare-backed Fruit Bat 109 arabicus, Rousettus aegyptiacus 87 Abruzzi’s Wrinkle-lipped Bat 645 albipinnis, Taphozous longimanus 353 Andersen’s Flying Fox 158 arabium, Rhinopoma cystops 176 Abyssinian Horseshoe Bat 290 albiventer, Nyctimene 36, 118 Andersen’s Fruit-eating Bat 578 Arafura Large-footed Bat 969 Acerodon albiventris, Noctilio 405, 411 Andersen’s Leaf-nosed Bat 254 Arata Yellow-shouldered Bat 543 Sulawesi 134 albofuscus, Scotoecus 762 Andersen’s Little Fruit-eating Bat 578 Arata-Thomas Yellow-shouldered Talaud 134 alboguttata, Glauconycteris 833 Andersen’s Naked-backed Fruit Bat 109 Bat 543 Acerodon 134 albus, Diclidurus 339, 367 Andersen’s Roundleaf Bat 254 aratathomasi, Sturnira 543 Acerodon mackloti (see A.
    [Show full text]
  • GRAY BAT Scientific Name: Myotis Grisescens Howell Other Commonly
    Common Name: GRAY BAT Scientific Name: Myotis grisescens Howell Other Commonly Used Names: gray myotis Previously Used Scientific Names: none Family: Vespertilionidae Rarity Ranks: G3/S1 State Legal Status: Endangered Federal Legal Status: Endangered Description: Color of the gray bat varies from dark gray immediately following molt in July or August, to russet, which is especially evident in females during the spring. Woolly-looking dorsal fur is uniformly gray from root to tip and the belly fur is grayish-white. The rear edge of the wing membrane attaches at the ankle. This is Georgia's largest Myotis bat, with a total length of 80 - 100 mm (3 - 4 inches), forearm length of 40 - 46 mm (1 -1 inches), wing spread of about 30 cm (12 inches) and weight of 7 - 16 grams (¼ - ½ ounces), typically 8 - 11 grams (about ¼ ounces). Similar Species: The gray bat is very similar to several other species in the same genus: southeastern bat (Myotis austroriparius), little brown bat (M. lucifugus), northern long-eared bat (M. septentrionalis), and Indiana bat (M. sodalis). However, these other myotis bats have banded dorsal fur (not uniformly colored from base to tip), and the wing membrane attaches to the base of the first toe rather than the ankle. Habitat: Perhaps the most cave-dependent mammal in this country, the gray bat roosts and hibernates exclusively in suitable caves in the southeastern U.S. However, some of the few specimens collected in Georgia were found in a drainage tunnel under the University of Georgia football stadium. Less than 5% of available caves in the southeastern U.S.
    [Show full text]
  • Gray Bat -- DRAFT Effects Determination Guidance for Endangered & Threatened Species (EDGES)
    DRAFT – Gray Bat -- DRAFT Effects Determination Guidance for Endangered & Threatened Species (EDGES) Bartow, Carroll, Catoosa, Chattooga, Cherokee, Clayton, Dade, Gilmer, Floyd, Gordon, Haralson, Murray, Paulding, Pickens, Polk, Rabun, Walker, Whitfield Counties Species Covered by This EDGES: • Endangered: Gray Bat The gray bat (Myotis grisescens) is federally listed as endangered (USFWS 1976). Its range includes the central and eastern United States, including northwest Georgia. Habitat destruction and modification are the primary causes of the decline of the species. Gray bats typically live in caves year-round. In winter, gray bats hibernate in caves that often have multiple entrances and good air flow (USFWS 2009). In the summer, gray bats roost in karst features, often along rivers. Gray bats have also been documented living in bridges and culverts in the summer and winter (Keeley and Tuttle 1999, K. Morris, pers. comm.). Gray bats emerge at night to forage in forested areas along banks of streams and lakes and may travel over 20 miles in a given night to feed. This species is highly dependent on aquatic insects, especially mayflies, caddisflies, stoneflies beetles, and moths (USFWS 2009). Gray bats clustered in Sitton’s Cave. Photo by Pete Pattavina. Breeding begins in the fall when the male gray bats arrive at hibernacula. Females do not become pregnant until emergence from hibernation in late March or early April. In late May or early June pregnant females give birth to a single pup that is capable of flight within 20 to 25 days (USFWS 2009). Newly volant gray bats travel up to 4 miles between roost caves and foraging areas.
    [Show full text]
  • GRAY and Indiana BAT POPULATION TRENDS in MISSOURI PE-44
    PE-44 Gray and Indiana Bat population Trends in Missouri William R. Elliott Cave Biologist/Resource Scientist Missouri Department of Conservation Resource Science Division Jefferson City, Missouri 65102-0180 [email protected] 573-751-4115 ext 3194 Abstract Since 1975 the Missouri Department of Conservation (MDC) has system- atically censused the endangered bats, Myotis sodalis (Indiana bat) and M. grise- scens (Gray bat). A recent statewide reestimate of about 15,812 indicates that Indiana bats declined by 95% since 1979. Pilot Knob Mine, a National Wildlife Refuge, had 80,000-100,000 Indiana bats in 1958, but only 1,678 were found there in February 2008, a 98% decline. At other sites they declined or abandoned one cave for another, seeking protection and more optimal temperatures. Their decline probably was caused by multiple factors, including human disturbance, the partial collapse of Pilot Knob Mine in 1979, warming of hibernacula, and possibly by pesticides and loss of summer habitat in northern Missouri. White Nose Syndrome has not been found in Missouri. Missouri’s Gray bat population declined, but it is now stable or increasing in some protected caves. Many other caves remain abandoned for various reasons. At bottom, Gray bats lost at least 67% of their maximum past population, as measured in 56 important caves, and 53% of the caves were abandoned. The ma- ternity population of Gray bats is currently estimated at approximately 635,000, but it may have been >1,700,000 in the past. The three largest Gray bat hiber- nacula were censused in 2006 and totalled 773,850.
    [Show full text]
  • Monitoring Trends in Bat Populations of the United States and Territories: Problems and Prospects: U.S
    MonitoringMonitoringMonitoring TTTrends in Bat Populations of the United SSthe tates andandtates TTTerritories:erritories:erritories: Problems and Prospects Information and Technology Report USGS/BRD/ITR–2003-0003 U.S. Department of the Interior U.S. Geological Survey To purchase this report, contact the National Technical Information Service, 5285 Port Royal Road, Springfield, VA 22161 (call toll free 1-800-553-6847), or the Defense Technical Information Center, 8725 Kingman Rd., Suite 0944, Fort Belvoir, VA 22060-6218. Cover photograph by Thomas J. O’Shea U.S. Geological Survey MonitoringMonitoringMonitoring TTTrends in Bat Populations of the United States andandtates TTTerritories:erritories:erritories: Problems and Prospects Information and Technology Report USGS/BRD/ITR–2003-0003 By T.J. O’Shea M.A. Bogan Editors U.S. Department of the Interior U.S. Geological Survey Suggested citation: O’Shea, T.J. and Bogan, M.A., eds., 2003, Monitoring trends in bat populations of the United States and territories: problems and prospects: U.S. Geological Survey, Biological Resources Discipline, Information and Technology Report, USGS/BRD/ITR--2003–0003, 274 p. ii ContentsContentsContents Page Introduction (T.J. O’Shea and M.A. Bogan) ............................................................................................ 1 Bats of the United States and Territories .......................................................................................................................2 Problems and Prospects for Monitoring Trends in Bat Populations
    [Show full text]
  • Georgia Cave Bat Identification Guide
    Georgia Cave Bat Identification Guide Photo by Pete Pattavina Original ID slides by Shelly Colatskie, Assistant Cave Ecologist, Missouri Department of Conservation Edited by Trina Morris & Jackie Jeffery, GA DNR Tri Colored Bat (Perimyotis subflavus) Pink forearms, [PESU] ears and nose. Photo by Pete Pattavina • Most common winter bat in GA • Roosts throughout the cave. • Typically roosts individually, but occasional in small clusters • Likes to roost in formations as well as holes and on cave wall and ceiling • Small bat • Is often seen covered in condensation Big Brown Bat (Eptesicus fuscus) [EPFU] Shiny brown Bare, dog like muzzle dorsal fur • Large and Robust • Typically roost outside entrance or inside entrance (in coldest sections of caves) • Most don’t hibernate in caves in GA – active in winter • Will roost individually or in small clusters. • Found in cracks, holes or on cave ceilings/walls • May intermingle with other species. Northern Long-eared Bat (Myotis septentrionalis) [MYSE] Dark Mask surrounding muzzle Long pointed tragus Pink Nose • Low numbers in caves but most common Myotis. • Large ears compared to other Myotis species. • Ears tend to be lighter in color than other Myotis species. • Sometimes pink-ish forearm. • Tend to roost in cracks, holes and crevices in caves. Can be seen roosting in clusters or single • Ventral side: fairly white • Dorsal side: light brown Little Brown Bat Shiny brown dorsal fur (Myotis lucifugus) [MYLU] Dark nose and ears • Rarely found in small numbers in N GA caves • Black nose • Typically shiny dorsal fur and white ventral fur • Usually dark ears • Can form dense clusters like Indianas, but typically smaller in size.
    [Show full text]
  • Immune Function and Metabolism of Hibernating North American Bats with White-Nose Syndrome
    BearWorks MSU Graduate Theses Summer 2018 Immune Function and Metabolism of Hibernating North American Bats with White-Nose Syndrome Briana Nicole Anderson Missouri State University, [email protected] As with any intellectual project, the content and views expressed in this thesis may be considered objectionable by some readers. However, this student-scholar’s work has been judged to have academic value by the student’s thesis committee members trained in the discipline. The content and views expressed in this thesis are those of the student-scholar and are not endorsed by Missouri State University, its Graduate College, or its employees. Follow this and additional works at: https://bearworks.missouristate.edu/theses Part of the Immunology of Infectious Disease Commons, Integrative Biology Commons, Other Genetics and Genomics Commons, and the Other Physiology Commons Recommended Citation Anderson, Briana Nicole, "Immune Function and Metabolism of Hibernating North American Bats with White-Nose Syndrome" (2018). MSU Graduate Theses. 3298. https://bearworks.missouristate.edu/theses/3298 This article or document was made available through BearWorks, the institutional repository of Missouri State University. The work contained in it may be protected by copyright and require permission of the copyright holder for reuse or redistribution. For more information, please contact [email protected]. IMMUNE FUNCTION AND METABOLISM OF HIBERNATING NORTH AMERICAN BATS WITH WHITE-NOSE SYNDROME A Masters Thesis Presented to The Graduate College of Missouri State University TEMPLATE In Partial Fulfillment Of the Requirements for the Degree Master of Science, Biology By Briana Anderson August 2018 Copyright 2018 by Briana Nicole Anderson ii IMMUNE FUNCTION AND METABOLISM OF HIBERNATING NORTH AMERICAN BATS WITH WHITE-NOSE SYNDROME Biology Missouri State University, August 2018 Master of Science Briana Anderson ABSTRACT White-nose syndrome (WNS) causes substantial mortality in certain species of hibernating North American bats.
    [Show full text]