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Comprehensive Conservation Plan Benton Lake National Wildlife
Glossary accessible—Pertaining to physical access to areas breeding habitat—Environment used by migratory and activities for people of different abilities, es- birds or other animals during the breeding sea- pecially those with physical impairments. son. A.D.—Anno Domini, “in the year of the Lord.” canopy—Layer of foliage, generally the uppermost adaptive resource management (ARM)—The rigorous layer, in a vegetative stand; mid-level or under- application of management, research, and moni- story vegetation in multilayered stands. Canopy toring to gain information and experience neces- closure (also canopy cover) is an estimate of the sary to assess and change management activities. amount of overhead vegetative cover. It is a process that uses feedback from research, CCP—See comprehensive conservation plan. monitoring, and evaluation of management ac- CFR—See Code of Federal Regulations. tions to support or change objectives and strate- CO2—Carbon dioxide. gies at all planning levels. It is also a process in Code of Federal Regulations (CFR)—Codification of which the Service carries out policy decisions the general and permanent rules published in the within a framework of scientifically driven ex- Federal Register by the Executive departments periments to test predictions and assumptions and agencies of the Federal Government. Each inherent in management plans. Analysis of re- volume of the CFR is updated once each calendar sults helps managers decide whether current year. management should continue as is or whether it compact—Montana House bill 717–Bill to Ratify should be modified to achieve desired conditions. Water Rights Compact. alternative—Reasonable way to solve an identi- compatibility determination—See compatible use. -
Aquatic Insect Ecophysiological Traits Reveal Phylogenetically Based Differences in Dissolved Cadmium Susceptibility
Aquatic insect ecophysiological traits reveal phylogenetically based differences in dissolved cadmium susceptibility David B. Buchwalter*†, Daniel J. Cain‡, Caitrin A. Martin*, Lingtian Xie*, Samuel N. Luoma‡, and Theodore Garland, Jr.§ *Department of Environmental and Molecular Toxicology, Campus Box 7633, North Carolina State University, Raleigh, NC 27604; ‡Water Resources Division, U.S. Geological Survey, 345 Middlefield Road, MS 465, Menlo Park, CA 94025; and §Department of Biology, University of California, Riverside, CA 92521 Edited by George N. Somero, Stanford University, Pacific Grove, CA, and approved April 28, 2008 (received for review February 20, 2008) We used a phylogenetically based comparative approach to evaluate ecosystems today (e.g., trace metals) (6). This variation in the potential for physiological studies to reveal patterns of diversity susceptibility has practical implications, because the ecological in traits related to susceptibility to an environmental stressor, the structure of aquatic insect communities is often used to indicate trace metal cadmium (Cd). Physiological traits related to Cd bioaccu- the ecological conditions in freshwater systems (7–9). Differ- mulation, compartmentalization, and ultimately susceptibility were ences among species’ responses to environmental stressors can measured in 21 aquatic insect species representing the orders be profound, but it is uncertain whether the cause is related to Ephemeroptera, Plecoptera, and Trichoptera. We mapped these ex- functional ecology [usually the assumption (10, 11)] or physio- perimentally derived physiological traits onto a phylogeny and quan- logical traits (5, 12–14), which have received considerably less tified the tendency for related species to be similar (phylogenetic attention. To the degree that either is involved, their link to signal). -
Abstract Poteat, Monica Deshay
ABSTRACT POTEAT, MONICA DESHAY. Comparative Trace Metal Physiology in Aquatic Insects. (Under the direction of Dr. David B. Buchwalter). Despite their dominance in freshwater systems and use in biomonitoring and bioassessment programs worldwide, little is known about the ion/metal physiology of aquatic insects. Even less is known about the variability of trace metal physiologies across aquatic insect species. Here, we measured dissolved metal bioaccumulation dynamics using radiotracers in order to 1) gain an understanding of the uptake and interactions of Ca, Cd and Zn at the apical surface of aquatic insects and 2) comparatively analyze metal bioaccumulation dynamics in closely-related aquatic insect species. Dissolved metal uptake and efflux rate constants were calculated for 19 species. We utilized species from families Hydropsychidae (order Trichoptera) and Ephemerellidae (order Ephemeroptera) because they are particularly species-rich and because they are differentially sensitive to metals in the field – Hydropsychidae are relatively tolerant and Ephemerellidae are relatively sensitive. In uptake experiments with Hydropsyche sparna (Hydropsychidae), we found evidence of two shared transport systems for Cd and Zn – a low capacity-high affinity transporter below 0.8 µM, and a second high capacity-low affinity transporter operating at higher concentrations. Cd outcompeted Zn at concentrations above 0.6 µM, suggesting a higher affinity of Cd for a shared transporter at those concentrations. While Cd and Zn uptake strongly co-varied across 12 species (r = 0.96, p < 0.0001), neither Cd nor Zn uptake significantly co-varied with Ca uptake in these species. Further, Ca only modestly inhibited Cd and Zn uptake, while neither Cd nor Zn inhibited Ca uptake at concentrations up to concentrations of 89 nM Cd and 1.53 µM Zn. -
100 Characters
40 Review and Update of Non-mollusk Invertebrate Species in Greatest Need of Conservation: Final Report Leon C. Hinz Jr. and James N. Zahniser Illinois Natural History Survey Prairie Research Institute University of Illinois 30 April 2015 INHS Technical Report 2015 (31) Prepared for: Illinois Department of Natural Resources State Wildlife Grant Program (Project Number T-88-R-001) Unrestricted: for immediate online release. Prairie Research Institute, University of Illinois at Urbana Champaign Brian D. Anderson, Interim Executive Director Illinois Natural History Survey Geoffrey A. Levin, Acting Director 1816 South Oak Street Champaign, IL 61820 217-333-6830 Final Report Project Title: Review and Update of Non-mollusk Invertebrate Species in Greatest Need of Conservation. Project Number: T-88-R-001 Contractor information: University of Illinois at Urbana/Champaign Institute of Natural Resource Sustainability Illinois Natural History Survey 1816 South Oak Street Champaign, IL 61820 Project Period: 1 October 2013—31 September 2014 Principle Investigator: Leon C. Hinz Jr., Ph.D. Stream Ecologist Illinois Natural History Survey One Natural Resources Way, Springfield, IL 62702-1271 217-785-8297 [email protected] Prepared by: Leon C. Hinz Jr. & James N. Zahniser Goals/ Objectives: (1) Review all SGNC listing criteria for currently listed non-mollusk invertebrate species using criteria in Illinois Wildlife Action Plan, (2) Assess current status of species populations, (3) Review criteria for additional species for potential listing as SGNC, (4) Assess stressors to species previously reviewed, (5) Complete draft updates and revisions of IWAP Appendix I and Appendix II for non-mollusk invertebrates. T-88 Final Report Project Title: Review and Update of Non-mollusk Invertebrate Species in Greatest Need of Conservation. -
New Distributional Records of Amphibians and Reptiles From
Check List 2(1) ISSN: 1809-127X NOTES ON GEOGRAPHIC DISTRIBUTION Insecta, Ephemeroptera: range extensions and Wedowee, 14-VI-1973, B. Stark; Site 4: Franklin new Alabama state records County, Little Bear Creek, at county road 23, 34°30’08” N 88°02’41” W, 19-III-2004, J Webb. W. P. McCafferty J. M. Webb Ephemerellidae Department of Entomology, Purdue University, Dannella provonshai (McCafferty). Site 4 (see West Lafayette, Indiana, U.S.A. 47907. E-mail: above). [email protected] Ephemerella excrucians Walsh. Site 4 (see The mayfly (Ephemeroptera) fauna of Alabama above). (U.S.A.) has been relatively well documented in terms of eastern North American regions, Ephemerella septentrionalis McDunnough. Site 4 primarily because of the contributions of Berner (see above). (1977), Kondratieff and Harris (1986), and Harris et al. (1996). Previously, 116 valid nominal Eurylophella macdunnoughi Funk. Site 4 (see species were reported from Alabama. That above). number takes into account recent significant synonymies that reduce the number of Alabama Isonychiidae species in the genera Drunella Needham (Jacobus and McCafferty 2003), Epeorus Eaton (Webb and Isonychia serrata Traver. Site 5: Cleburne McCafferty 2006), and Ephemerella Walsh County, South of Chulafinnee, Highway 431, 14- (Jacobus and McCafferty 2003). Herein we VI-1973, B. Stark (adults); Site 6: Shelby County, augment the recorded fauna with eleven Northwest of Harpersville, Highway 280, 14-VI- additional species taken from eight counties 1973, B. Stark (adults). representative of the four northern physiographic provinces in the state (see Kondratieff and Harris Isonychia sicca (Walsh): Site 4 (see above). 1986), including the Highland Rim Plateau, the Cumberland Plateau, the Valley and Ridge, and Isonychia tusculanensis Berner. -
Mayflies in a Changing World
MAYFLY POPULATION DENSITY, PERSISTENCE AND GENETIC STRUCTURE IN FRAGMENTED HEADWATER HABITATS L. C. Alexander and W. O. Lamp Department of Entomology, University of Maryland, College Park, Maryland 20742 USA Abstract We assessed the effects of stream habitat loss and fragmentation on the density, genetic diversity and persistence of a mayfly (Ephemerella inconstans Traver, 1932) in 24 first-order streams across nine headwater stream networks in Maryland and Virginia. We present differences in population density and local extinction in forested versus deforested headwater streams, as well as a preliminary analysis of genetic diversity in populations of E. inconstans and three closely related species. Because the sampling period spanned two years of drought (2001–2002) followed by two years of recovery (2003–2004), we predicted that mayfly density would be higher and population extinction rates lower at forested sites compared with deforested (agricultural and residential) sites. We found no difference in initial density at forested and deforested sites and no difference in the level of population decline across all sites by the end of the drought. However, one year after the drought had ended, population density was significantly higher in forested streams compared with streams flowing through agricultural and residential areas. Further, while only 1 of 11 populations at forested sites remained extirpated in 2004, populations in 4 of the 13 deforested streams were extirpated at the end of the study. These results suggest that recovery and recolonization following a major regional disturbance was more successful in the intact, forested stream networks than in the altered networks. To examine the population genetic effects of the demographic decline, extinction events and post-drought recovery, we sequenced a region of mitochondrial DNA in 10 populations. -
A Revision of the Genus Ephemerella (Ephemeroptera, Ephemerellidae) VIII
OF THE '~ ' . ' . " VOLUME 4 NUMBER 6 APRIL, 1965 .. :· ·, ..... Published by the ENTOMOLOGICAL SOCIETY OF A1'1ERICA A Revision of the Genus Ephemerella (Ephemeroptera, Ephemerellidae) VIII. The Subgenus Ephemerella in North America RICHARD K. ALLEN AND GEORGE F. EDMUNDS, JR. CONTENTS Abstract 244 E. fratcrcula McDunnough . 264 rntrocluction 244 E. nzollitia Seemann. ................. 265 Taxonomy 244 E. lacustris, n. sp .. 265 Keys to the North American subgenera of E. inernzis Eaton. 267 Ephcnicrclla 244 E. i11Jrequens McDunnough. 271 Subgenus E phcmcrclla "Talsh s. s. 245 E. maculata Traver ........ 273 Keys to the l\' orth American species of the E. needhami McDunnough. 274 subgenus E phemerella 247 Ji. aurivillii (Bengtsson) 27.5 Ji. catawba Traver 253 E. 1•erruca, n. sp ... 276 E. excrucians Walsh. 256 Ji. crcnula, n. sp .. 277 E. ora Burks 256 E. sinzila, 11. sp .. 277 !~. argo Burks 258 E. rossi, 11. sp. 278 E. dorothea Needham 258 E. hispida, n. sp .. 278 E. inconstans Traver 2S9 E. bcrneri Allen and Edmunds. 278 Ji. subvaria McDunnough 260 E. septentrionalis McDunnough. 279 E. rotunda Morgan 261 Acknowledgments 279 E. invaria (Walker) 263 E. choctawhatchee Berner 264 References Cited ....................... 280 A Revision of the Genus Ephemerella (Ephemeroptera, Ephemerellidae) VIII. The Subgenus Ephemerella in North America Rrc:HARD K. ALLEN AND CEOR<;E F. EDM u :-ms, J R. 1 Uniz'crsity of Utah, Salt La!.'c City, Utah ABSTRACT The 25 species of the genus Ephemerella Walsh in tions, and distribution records and maps. Illustrated keys North America formerly placed in the subgenera Ephem arc given for the nymphs and male a(lults. -
2015 Illinois Wildlife Action Plan Implementation Guide
2015 Implementation Guide to the As Prescribed by The Wildlife Conservation and Restoration Program and the State Wildlife Grant Program Illinois Wildlife Action Plan 2015 Implementation Guide Table of Contents I. Acknowledgments IG vi II. Foreword IG vii III. Introduction IG 1 IV. Species in Greatest Conservation Need SGCN 6 a. Table 1. Summary of Illinois’ SGCN by taxonomic group SGCN 8 V. Conservation Opportunity Areas a. Description COA 9 b. What are Conservation Opportunity Areas COA 9 c. Status as of 2015 COA 10 d. Ways to accomplish work COA 11 e. Table 2. Summary of the 2015 status of individual COAs COA 14 f. Table 3. Importance of conditions for planning and implementation COA 15 g. Table 4. Satisfaction of conditions for planning and implementation COA 16 h. Figure 1. COAs currently recognized through Illinois Wildlife Action Plan COA 17 i. Figure 2. Factors that contribute or reduce success of management COA 18 j. Figure 3. Intersection of COAs with Campaign focus areas COA 19 k. References COA 20 VI. Campaigns Campaign 21 a. Farmland and Prairie i. Description F&P 22 ii. Goals and Current Status as of 2015 F&P 22 iii. Stresses and Threats to Wildlife and Habitat F&P 26 iv. Focal Species F&P 30 v. Actions F&P 31 vi. Focus Areas F&P 37 vii. Management Resources F&P 39 viii. Performance Measures F&P 41 ix. References F&P 42 x. Table 5. Breeding Bird Survey Data F&P 44 xi. Figure 4. Amendment to Mason Co. Sands COA F&P 45 xii. -
2015 Lower Belt Creek – Coal Acid Mine Drainage Sampling Report
2015 Lower Belt Creek – Coal Acid Mine Drainage Sampling Report Final Report for Montana Department of Environmental Quality Prepared by Jason Mullen, Montana Fish, Wildlife & Parks Trevor Selch, Montana Fish, Wildlife & Parks Lindsey Gilstrap, Montana Fish, Wildlife & Parks Dylan Owensby, Montana Fish, Wildlife & Parks February 2018 Introduction Acid mine drainage (AMD) from past coal mining activities currently results in exceedances of Montana Water Quality Standards for iron and aluminum in Belt Creek, in the town of Belt, Montana. Numerous other metals exceed the water quality standards in the AMD water itself. Montana Department of Environmental Quality (MDEQ) is proposing to construct a water treatment plant in the area of Coke Oven Flats to treat several sources of AMD water prior to it reaching Belt Creek and thereby improve water quality in Belt Creek. Currently, water quality monitoring is being conducted by MDEQ; however, no aquatic life (fish and benthic invertebrate) monitoring had been conducted in Belt Creek in this area. Montana Fish, Wildlife and Parks (MFWP) sought to begin fish and benthic invertebrate monitoring to document the level of impact prior to construction of the treatment plant. With continued monitoring following the construction of the treatment plant, MFWP will provide documentation of the response in the aquatic life, which is one of the designated beneficial uses of Belt Creek. Methods and Study Area Fish Sampling We sampled fish populations in the sections immediately upstream (control) and downstream (impact) from the AMD site (considered the Anaconda discharge for this report) in Belt Creek on November 2, 2015 (Figure 1 and Table 1). -
Macroinvertebrate Monitoring for the Upper Missouri River: Building a Long-Term Data Set 2015-2019
UMOWA Missouri River Project Baseline Aquatic Surveys Montana Biological Survey April 2020 Macroinvertebrate Monitoring for the Upper Missouri River: Building a Long-term Data Set 2015-2019 Prepared for: Alan Shaw, Sherry Meador, Pete Petersen, Pat Hunter and Bailey Sory Project Managers/Co-Chairs Missouri River Monitoring Station below the Dearborn River Fall 2019 Prepared by: David Stagliano, Aquatic Ecologist Montana Biological Survey Helena, Montana April 2020 UMOWA Missouri River Project Baseline Aquatic Macroinvertebrate Surveys Montana Biological Survey April 2020 Table of Contents Acknowledgements .................................................................................................................................... 3 Executive Summary ................................................................................................................................... 4 1.0 Introduction ........................................................................................................................................... 6 2.0 Methods ................................................................................................................................................ 8 2.1 Habitat and Physical Water Sampling .......................................................................................... 8 2.2 Macroinvertebrate Sampling .......................................................................................................... 8 2.3 Taxonomic Analysis ....................................................................................................................... -
Appendix for Benton Lake National Wildlife Refuge Complex Draft
Glossary accessible—Pertaining to physical access to areas canopy—Layer of foliage, generally the uppermost and activities for people of different abilities, es layer, in a vegetative stand; midlevel or under pecially those with physical impairments. story vegetation in multilayered stands. Canopy A .D .—Anno Domini, “in the year of the Lord.” closure (also canopy cover) is an estimate of the adaptive resource management (ARM)—The rigorous amount of overhead vegetative cover. application of management, research, and moni CCP—See comprehensive conservation plan. toring to gain information and experience neces CFR—See Code of Federal Regulations. sary to assess and change management activities. CO2—Carbon dioxide. It is a process that uses feedback from research, Code of Federal Regulations (CFR)—Codification of monitoring, and evaluation of management ac the general and permanent rules published in the tions to support or change objectives and strate Federal Register by the Executive departments gies at all planning levels. It is also a process in and agencies of the Federal Government. Each which the Service carries out policy decisions volume of the CFR is updated once each calendar within a framework of scientifically driven ex year. periments to test predictions and assumptions compact—Montana House bill 717–Bill to Ratify inherent in management plans. Analysis of re Water Rights Compact. sults helps managers decide whether current compatibility determination—See compatible use. management should continue as is or whether it compatible use—Wildlife-dependent recreational should be modified to achieve desired conditions. use or any other use of a refuge or district that, alternative—Reasonable way to solve an identi in the sound professional judgment of the Direc fied problem or satisfy the stated need (40 CFR tor of the U.S. -
Invertebrates
Pennsylvania’s Comprehensive Wildlife Conservation Strategy Invertebrates Version 1.1 Prepared by John E. Rawlins Carnegie Museum of Natural History Section of Invertebrate Zoology January 12, 2007 Cover photographs (top to bottom): Speyeria cybele, great spangled fritillary (Lepidoptera: Nymphalidae) (Rank: S5G5) Alaus oculatus., eyed elater (Coleoptera: Elateridae)(Rank: S5G5) Calosoma scrutator, fiery caterpillar hunter (Coleoptera: Carabidae) (Rank: S5G5) Brachionycha borealis, boreal sprawler moth (Lepidoptera: Noctuidae), last instar larva (Rank: SHG4) Metarranthis sp. near duaria, early metarranthis moth (Lepidoptera: Geometridae) (Rank: S3G4) Psaphida thaxteriana (Lepidoptera: Noctuidae) (Rank: S4G4) Pennsylvania’s Comprehensive Wildlife Conservation Strategy Invertebrates Version 1.1 Prepared by John E. Rawlins Carnegie Museum of Natural History Section of Invertebrate Zoology January 12, 2007 This report was filed with the Pennsylvania Game Commission on October 31, 2006 as a product of a State Wildlife Grant (SWG) entitled: Rawlins, J.E. 2004-2006. Pennsylvania Invertebrates of Special Concern: Viability, Status, and Recommendations for a Statewide Comprehensive Wildlife Conservation Plan in Pennsylvania. In collaboration with the Western Pennsylvania Conservancy (C.W. Bier) and The Nature Conservancy (A. Davis). A Proposal to the State Wildlife Grants Program, Pennsylvania Game Commission, Harrisburg, Pennsylvania. Text portions of this report are an adaptation of an appendix to a statewide conservation strategy prepared as part of federal requirements for the Pennsylvania State Wildlife Grants Program, specifically: Rawlins, J.E. 2005. Pennsylvania Comprehensive Wildlife Conservation Strategy (CWCS)-Priority Invertebrates. Appendix 5 (iii + 227 pp) in Williams, L., et al. (eds.). Pennsylvania Comprehensive Wildlife Conservation Strategy. Pennsylvania Game Commission and Pennsylvania Fish and Boat Commission. Version 1.0 (October 1, 2005).