James River Watershed Risk Analysis
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Powerlessness and Pollution in Alleghany County, Virginia: A
Powerlessness and Pollution in Alleghany County, Virginia: A Historical Analysis of Paternalism and Economic Coercion in Appalachia and its Relationship with Environmental Degradation Corey Lee Wrenn Thesis submitted to the faculty of the Virginia Polytechnic Institute and State University in partial fulfillment of the requirements for the degree of Master of Science In Sociology Committee: Toni Calasanti, Co-Chair Barbara Ellen Smith, Co-Chair Carl Riden of Longwood University August 6, 2008 Blacksburg, VA Keywords: paternalism, economic coercion, economic dependence, environment, labor relations, unionism, Appalachia Powerlessness and Pollution in Alleghany County, Virginia: A Historical Analysis of Paternalism and Economic Coercion in Appalachia and its Relationship with Environmental Degradation Corey Lee Wrenn Abstract Alleghany County, an extractive community, has depended heavily upon a single paper mill known as MeadWestvaco for over a century. The purpose of this study is to explore the degree to which MeadWestvaco utilizes paternalism and economic coercion as forms of power to control and maintain community quiescence regarding the company’s negative environmental impact in Alleghany County. This paper mill has negatively affected Alleghany County relative to other Virginia communities. However, there has been very little local action against the paper mill’s environmental impact. To define and recognize paternalism and economic coercion, I undertake a historical analysis of the cotton textile industry of the Southern Piedmont and coal mining industry of Southern Appalachia, where these systems of power have been documented. In applying the indicators of paternalism and economic coercion found in these nearby Southern industries to Alleghany County, Virginia, I find that MeadWestvaco utilizes both strategies to some degree to control and influence community awareness of and response to the company’s environmental damage. -
HAMPTON ROADS CLOSURES on WATER CROSSINGS, INTERSTATES and OTHER NOTABLE DETOURS for the Week of Jan
RELEASE: IMMEDIATE Dec. 31, 2020 CONTACT: Media Line: 757-956-3032 [email protected] HAMPTON ROADS CLOSURES ON WATER CROSSINGS, INTERSTATES AND OTHER NOTABLE DETOURS For the week of Jan. 3-9 NOTE: This list covers full closures of interstates, ramps, bridges and primary roads, and lane closures at the bridge-tunnels and the Berkley, Coleman, High Rise and James River bridges. *Scheduled closures are subject to change based on weather conditions and other factors.* For information on the many other lane closures necessary for maintenance and construction throughout Hampton Roads, visit 511Virginia.org, download the 511VA smartphone app, or dial 511. Bridges & Tunnels: Monitor-Merrimac Memorial Bridge-Tunnel, I-664: Single-lane closures northbound on Jan. 4-5 as early as 8 p.m. to 5 a.m. Single-lane closures southbound on Jan. 4-7 as early as 8 p.m. to 5 a.m. Alternating, mobile, single-lane closures northbound on Jan. 6 from 9 p.m. to 5 a.m. James River Bridge, Route 17: Single-lane closures in both directions on Jan. 4 from noon to 3 p.m. and on Jan. 5-8 from 9 a.m. to 3 p.m. HRBT Expansion Project: For lane closures and project updates related to the HRBT Expansion Project, visit HRBTExpansion.org. Elizabeth River Tunnels (Downtown/Midtown Tunnels): Go to Elizabeth River Tunnels for maintenance schedules on the Downtown Tunnel (I-264), Midtown Tunnel (U.S. 58) and MLK Expressway (Route 164). I-64 Widening Segment III Project, York County: Lane closures under flagger control on Lakeshead Drive at the I-64 overpasses on Jan. -
Endangered Species
FEATURE: ENDANGERED SPECIES Conservation Status of Imperiled North American Freshwater and Diadromous Fishes ABSTRACT: This is the third compilation of imperiled (i.e., endangered, threatened, vulnerable) plus extinct freshwater and diadromous fishes of North America prepared by the American Fisheries Society’s Endangered Species Committee. Since the last revision in 1989, imperilment of inland fishes has increased substantially. This list includes 700 extant taxa representing 133 genera and 36 families, a 92% increase over the 364 listed in 1989. The increase reflects the addition of distinct populations, previously non-imperiled fishes, and recently described or discovered taxa. Approximately 39% of described fish species of the continent are imperiled. There are 230 vulnerable, 190 threatened, and 280 endangered extant taxa, and 61 taxa presumed extinct or extirpated from nature. Of those that were imperiled in 1989, most (89%) are the same or worse in conservation status; only 6% have improved in status, and 5% were delisted for various reasons. Habitat degradation and nonindigenous species are the main threats to at-risk fishes, many of which are restricted to small ranges. Documenting the diversity and status of rare fishes is a critical step in identifying and implementing appropriate actions necessary for their protection and management. Howard L. Jelks, Frank McCormick, Stephen J. Walsh, Joseph S. Nelson, Noel M. Burkhead, Steven P. Platania, Salvador Contreras-Balderas, Brady A. Porter, Edmundo Díaz-Pardo, Claude B. Renaud, Dean A. Hendrickson, Juan Jacobo Schmitter-Soto, John Lyons, Eric B. Taylor, and Nicholas E. Mandrak, Melvin L. Warren, Jr. Jelks, Walsh, and Burkhead are research McCormick is a biologist with the biologists with the U.S. -
Roanoke Region Outdoor Impact, Infrastructure and Investment
Roanoke Region Outdoor Impact, Infrastructure and Investment Prepared for the Roanoke Regional Partnership & Roanoke Outside Foundation| August 2018 Table of Contents 04 About This Report 08 Executive Summary Business & Talent Wage Growth Attraction 12 The Case 20 Recommendations 30 Funding Structure Attractive Outdoor Impact Tourism Environment 38 Organizational Structure 44 Best Practices Healthy Global Brand Community Recognition 50 Supporting Data 60 Survey Results and National Trends 3 About This Report Avalanche Consulting, a leader in economic development consulting, and GreenPlay, a consortium of experts on parks, recreation, and open spaces, utilized research, local community input, and national studies and trends to create this report for the Roanoke Region of Virginia. Recommendations contained within this report are intended to be a blueprint for both public and private sector investment to support future growth of the region. This report includes the following: • The Case – Background information and context that shows why there is an urgent need for outdoor infrastructure investments in the region and a summary of goals and strategies to take the region’s outdoor assets to the next level. • Recommendations – A look at actionable elements and specific goals, strategies, and tactics related to investing in outdoor infrastructure, engaging the community, marketing outdoor assets to business and talent, and attracting and supporting businesses that complement the outdoor economy, ultimately setting the region up for long-term economic prosperity. • Funding and Organizational Structure – Organization and funding options are a key component to optimize a program focused on enhancing, maintaining, and sustaining outdoor infrastructure and the region’s competitive advantage. • Best Practices – Examples of organization and funding sources are outlined, including the Anacostia River Clean Up and Protection Fund, Outdoor Knoxville, and Oklahoma City MAPS. -
Species of Greatest Conservation Need
APPENDIX A. VIRGINIA SPECIES OF GREATEST CONSERVATION NEED Taxa Common Scientific Name Tier Cons. Opp. Habitat Descriptive Habitat Notes Name Ranking Amphibians Barking Hyla gratiosa II a Forest Forests near or within The Virginia Fish and Wildlife Information System indicates treefrog shallow wetlands the loss suitable wetlands constitute the greatest threats to this species. DGIF recommends working to maintain or restore forested buffers surrounding occupied wetlands. These needs are consistent with action plan priorities to conserve and restore wetland habitats and associated buffers. Recently discovered populations within its known range, may indicate this species is more abundant than previously believed. An in-depth investigation into its status may warrant delisting. This species will be prioritized as Tier 2a. Amphibians Blue Ridge Desmognathus IV c Forest High elevation seeps, This species' distribution is very limited. Other than limiting dusky orestes streams, wet rock faces, logging activity in the occupied areas, no conservation salamander and riparian forests actions have been identified. Unless other threats or actions are identified, this species will be listed as Tier 4c. Amphibians Blue Ridge Eurycea III a Wetland Mountain streams and The needs of this species are consistent with priorities for two-lined wilderae adjacent riparian areas maintaining and enhancing riparian forests and aquatic salamander with mixed hardwood or habitats. This species will be listed as Tier 3a. spruce-fir forests up to 6000 feet. Amphibians Carpenter Lithobates III a Wetland Freshwater wetlands with The needs of this species are consistent with action plan frog virgatipes sphagnum moss priorities to preserve and restore aquatic and wetland habitats and water quality. -
255 James River Basin 02011400 Jackson River Near Bacova
JAMES RIVER BASIN 255 02011400 JACKSON RIVER NEAR BACOVA, VA LOCATION.--Lat 38°02'32", long 79°52'53", NAD83, Bath County, Hydrologic Unit 02080201, on left bank 0.1 mi downstream from ford, 1.8 mi upstream from Back Creek, and 2.2 mi southwest of Bacova. DRAINAGE AREA.--158 mi2. WATER-DISCHARGE RECORDS PERIOD OF RECORD.--October 1974 to current year. GAGE.--Water-stage recorder. Datum of gage is 1,639.20 ft NGVD of 1929. REMARKS.--Records good except those for estimated daily discharges, which are fair. U.S. Army Corps of Engineers satellite water temperature, precipitation and gage-height telemeter at station. Maximum discharge, 30,000 ft3/s, from rating curve extended above 1,300 ft3/s on basis of slope-area measurements at gage heights 8.88 ft, 11.40 ft, 13.88 ft, and 22.25 ft. Minimum gage height, 2.42 ft, Aug. 18, 19, 1988. EXTREMES OUTSIDE PERIOD OF RECORD.--Flood of June 21, 1972, reached a stage of 11.40 ft, discharge, 4,800 ft3/s, and flood of Dec. 26, 1973, reached a stage of 13.88 ft, discharge, 7,560 ft3/s, from rating curve extended as explained above. PEAK DISCHARGES FOR CURRENT YEAR.--Peak discharges greater than base discharge of 1,500 ft3/s and maximum (*): Discharge Gage height Discharge Gage height Date Time (ft3/s) (ft) Date Time (ft3/s) (ft) Mar 28 1845 *2,310 *8.65 No other peak greater than base discharge. DISCHARGE, CUBIC FEET PER SECOND WATER YEAR OCTOBER 2004 TO SEPTEMBER 2005 DAILY MEAN VALUES DAY OCT NOV DEC JAN FEB MAR APR MAY JUN JUL AUG SEP 1 344 64 858 126 87 145 426 601 93 106 123 58 2 252 62 709 117 -
Special Structures
SPECIAL STRUCTURES Garrett Moore, PE July 17, 2018 Chief Engineer Keep Virginia Moving Virginia Department of Transportation Chapter 2 (2018) Requirements for Virginia’s Large & Unique Bridge and Tunnel Structures • CTB Report by December 1, 2018 • Overall condition • Funding needs • Recommendations for addressing funding* within the State of Good Repair program • Assess the Impact of • Establishing a set-aside from the State of Good Repair program • Limited use of allowing district minimum cap waiver (§33.2-369(B)) • Other options the Board identifies *Eligibility Virginia Department of Transportation Special Structures Challenges • Currently no dedicated funding mechanism in code • Typically do not qualify as structurally deficient • Legislative requirement for State of Good Repair (SGR) funding • No end of life decision protocol within current code • Continue to maintain • Rebuild • SGR fund not big enough • Potential for Reserve Fund Virginia Department of Transportation Special Structures Challenges Special Structure Needs Estimated $1.7 B over 30 years in FY 2017 dollars Projected FY 2019 – FY 2024 - $961 M* or SGR Funding Projected ITD - FY 2017 – FY 2024 - $1.1 B *935 Structurally Deficient Bridges as of July 1, 2017 (851 as of July 10, 2018) Structurally Deficient Bridges 243 funded with State of Good Repair 326 funded with other funds Virginia Department of Transportation What Makes Structures Special • Risk (Fracture-Critical) • Complexity • Maintenance Cost • Importance • Long Detours • High Traffic • Economic Significance -
BRM SOP Part V 20110408
Part V: Scoring Criteria for the Index of Biotic Integrity and the Index of Well-Being to Monitor Fish Communities in Wadeable Streams in the Coosa and Tennessee River Basins of the Blue Ridge Ecoregion of Georgia Georgia Department of Natural Resources Wildlife Resources Division Fisheries Management Section Stream Survey Team May 23, 2013 1 Table of Contents Introduction……………………………………………………………….…...3 Figure 1: Map of Blue Ridge Ecoregion………………………….………..…6 Table 1: Listed Fish in the Blue Ridge Ecoregion………………………..…..7 Table 2: Metrics and Scoring Criteria………………………………..….…....8 Table 3: Iwb Metric and Scoring Criteria………………………….…….…..10 Figure 2: Multidimensional scaling ordination plot……………………….....11 Table 4: High Elevation criteria……………………………………….….....12 References………………………………………………………...………….13 Appendix A……………………………………………………………..……A1 Appendix B……………………………………………………….………….B1 2 Introduction The Blue Ridge ecoregion (BRM), one of Georgia’s six Level III ecoregions (Griffith et al. 2001), forms the boundary for the development of this fish index of biotic integrity (IBI). Encompassing approximately 2,639 mi2 in northeast Georgia, the BRM includes portions of four major river basins — the Chattahoochee (CHT, 142.2 mi2), Coosa (COO, 1257.5 mi2), Savannah (SAV, 345.3 mi2), and Tennessee (TEN, 894.2 mi2) — and all or part of 16 counties (Figure 1). Due to the relatively small watershed areas and physical and biological parameters of the CHT and SAV basins within the BRM, and the resulting low number of sampled sites, IBI scoring criteria have not been developed for these basins. Therefore, only sites in the COO and TEN basins, meeting the criteria set forth in this document, should be scored with the following metrics. The metrics and scoring criteria adopted for the BRM IBI were developed by the Georgia Department of Natural Resources, Wildlife Resources Division (GAWRD), Stream Survey Team using data collected from 154 streams by GAWRD within the COO (89 sites) and TEN (65 sites) basins. -
Athletics | Directions
Alliance Christian School 5809 Portsmouth Blvd. Portsmouth, VA 757- 488- 5552 Take I-64 east to I-664 Take I-664 through Monitor-Merrimac tunnel Get off Portsmouth Blvd. ( Portsmouth) - exit 11B Go straight for about 4 miles and look for the school on the right Soccer games are held at Hodges Manor Elementary School:1201 CHerokee Rd. Portsmouth, VA 23701 (757) 465-2921 Merge onto I-664 E toward Norfolk Merge onto I-664 S/Hampton Roads Belt via exit 264 toward Downtown Newport News/Suffolk/Chespeake Merge onto VA-337 E/Portsmouth Blvd via exit 11B toward Portsmouth Turn right onto Elmhurst Lane Turn right onto Cherokee Road Tennis and Golf are played at Portsmouth City Park at City Park Ave., Portsmouth, VA 23321 Amelia Academy Merge onto I-64 W via the ramp on the LEFT toward RICHMOND. Take the I-295 S / US-60 exit- EXIT 200- toward ROCKY MT NC. Merge onto VA-895 W / POCAHONTAS PKWY via EXIT 25 toward RICHMOND (Portions toll). Keep LEFT to take VA- 150 N / CHIPPENHAM PKWY. Merge onto US-360 W toward AMELIA. Turn LEFT onto VA-153. Turn RIGHT onto VA-38. End at Amelia Academy . Atlantic Shores School 1217 N. Centerville Turnpike Chesapeake, VA 23320 757-479-3110 Take I-64 East to 2 nd Indian River Road exit and just past Founders Inn turn right on Centerville Turnpike and the school is 1 mile past the intersection of Kempsville Rd. on the left. If you come by I-664: Take I-64 West towards Virginia Beach Take 1 st Indian River Road exit Turn right on Centerville Turnpike and the school is 1 mile past the intersection of Kempsville Rd. -
Endangered Species
FEATURE: ENDANGERED SPECIES Conservation Status of Imperiled North American Freshwater and Diadromous Fishes ABSTRACT: This is the third compilation of imperiled (i.e., endangered, threatened, vulnerable) plus extinct freshwater and diadromous fishes of North America prepared by the American Fisheries Society’s Endangered Species Committee. Since the last revision in 1989, imperilment of inland fishes has increased substantially. This list includes 700 extant taxa representing 133 genera and 36 families, a 92% increase over the 364 listed in 1989. The increase reflects the addition of distinct populations, previously non-imperiled fishes, and recently described or discovered taxa. Approximately 39% of described fish species of the continent are imperiled. There are 230 vulnerable, 190 threatened, and 280 endangered extant taxa, and 61 taxa presumed extinct or extirpated from nature. Of those that were imperiled in 1989, most (89%) are the same or worse in conservation status; only 6% have improved in status, and 5% were delisted for various reasons. Habitat degradation and nonindigenous species are the main threats to at-risk fishes, many of which are restricted to small ranges. Documenting the diversity and status of rare fishes is a critical step in identifying and implementing appropriate actions necessary for their protection and management. Howard L. Jelks, Frank McCormick, Stephen J. Walsh, Joseph S. Nelson, Noel M. Burkhead, Steven P. Platania, Salvador Contreras-Balderas, Brady A. Porter, Edmundo Díaz-Pardo, Claude B. Renaud, Dean A. Hendrickson, Juan Jacobo Schmitter-Soto, John Lyons, Eric B. Taylor, and Nicholas E. Mandrak, Melvin L. Warren, Jr. Jelks, Walsh, and Burkhead are research McCormick is a biologist with the biologists with the U.S. -
Reproductive Biology and Host Requirement Differences
REPRODUCTIVE BIOLOGY AND HOST REQUIREMENT DIFFERENCES AMONG ISOLATED POPULATIONS OF CYPROGENIA ABERTI (CONRAD, 1850) A Thesis Presented to The Graduate College of Southwest Missouri State University In Partial Fulfillment of the Requirements for the Master of Science, Biology By Nathan L. Eckert August 2003 REPRODUCTIVE BIOLOGY AND HOST REQUIREMENT DIFFERENCES AMONG ISOLATED POPULATIONS OF CYPROGENIA ABERTI (CONRAD, 1850) Biology Department Southwest Missouri State University, August 2003 Master of Science Nathan L. Eckert ABSTRACT Cyprogenia aberti, the Western fanshell, is a rare and threatened pearly mussel endemic to the Interior Highlands of Eastern North America. Previous genetic analysis suggested that multiple species are present within this taxon. The present study sought phenotypic differences among genetically distinct populations in the upper Arkansas River system (Verdigris and Spring rivers), the St. Francis River, and the Ouachita River. Like other native mussels, the glochidia larvae of Cyprogenia are obligate parasites on particular species of host fish. Transformation success of glochidia was compared among 8 species of Percina and Etheostoma. The percentage of attached glochidia that transformed on individual fish ranged between 0 and 86%. Effective hosts (those that transformed a large proportion of attached glochidia) were always sympatric with the mussel population, and species with narrow geographic range were effective hosts only for sympatric mussel populations. However, two populations of a geographically widespread host species, the logperch, were effective hosts for each mussel population tested. The timing of glochidia and juvenile drop-off appeared to be related to the age or maturity of the glochidia. Glochidia size and shape differed among mussel populations. Conglutinate color, which is determined by the color of undeveloped eggs, varied within and among populations. -
Species Diversity Report George Washington National Forest Draft EIS April 2011
Appendix F - Species Diversity Report George Washington National Forest Draft EIS April 2011 U.S. Department of Agriculture Forest Service Southern Region Species Diversity Report George Washington National Forest April 2011 Appendix F - Species Diversity Report George Washington National Forest Draft EIS April 2011 Table of Contents Table of Contents ........................................................................................................................... i 1.0 Introduction ............................................................................................................................ 5 2.0 Species Diversity..................................................................................................................... 5 2.1 Ecosystem Context for Species ............................................................................................ 5 2.2 Identification and Screening of Species ............................................................................... 6 3.0 Threatened and Endangered Species ................................................................................... 7 3.1 Threatened and Endangered Species List ............................................................................ 7 3.2 Threatened and Endangered Species Descriptions and Plan Components .......................... 8 3.2.1 Indiana Bat ........................................................................................................................ 8 3.2.2 Virginia Big-Eared Bat ..................................................................................................