National Water Summary Wetland Resources: Georgia
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Okefenokee Swamp and St. Marys River Named Among America's
Okefenokee Swamp and St. Marys River named Among America’s Most Endangered Rivers of 2020 Mining threatens, fish and wildlife habitat; wetlands; water quality and flow Contact: Ben Emanuel, American Rivers, 706-340-8868 Christian Hunt, Defenders of Wildlife 828-417-0862 Rena Ann Peck, Georgia River Network, 404-395-6250 Alice Miller Keyes, One Hundred Miles, 912-230-6494 Alex Kearns, St. Marys EarthKeepers, 912-322-7367 Washington, D.C. –American Rivers today named the Okefenokee Swamp and St. Marys River among America’s Most Endangered Rivers®, citing the threat titanium mining would pose to the waterways’ clean water, wetlands and wildlife habitat. American Rivers and its partners called on the U.S. Army Corps of Engineers and other permitting agencies to deny any proposals that risk the long-term protection of the Okefenokee Swamp and St. Marys River. “America’s Most Endangered Rivers is a call to action,” said Ben Emanuel, Atlanta- based Clean Water Supply Director with American Rivers. “Some places are simply too precious to allow risky mining operations, and the edge of the unique Okefenokee Swamp is one. The Army Corps of Engineers must deny the permit to save this national treasure.” The annual America’s Most Endangered Rivers report is a list of rivers at a crossroads, where key decisions in the coming months will determine the rivers’ fates. Over the years, the report has helped spur many successes including the removal of outdated dams, the protection of rivers with Wild and Scenic designations, and the prevention of harmful development and pollution. Rena Ann Peck, Executive Director of Georgia River Network, explains "The Okefenokee Swamp is like the heart of the regional Floridan aquifer system in southeast Georgia and northeast Florida. -
Missouri River Floodplain from River Mile (RM) 670 South of Decatur, Nebraska to RM 0 at St
Hydrogeomorphic Evaluation of Ecosystem Restoration Options For The Missouri River Floodplain From River Mile (RM) 670 South of Decatur, Nebraska to RM 0 at St. Louis, Missouri Prepared For: U. S. Fish and Wildlife Service Region 3 Minneapolis, Minnesota Greenbrier Wetland Services Report 15-02 Mickey E. Heitmeyer Joseph L. Bartletti Josh D. Eash December 2015 HYDROGEOMORPHIC EVALUATION OF ECOSYSTEM RESTORATION OPTIONS FOR THE MISSOURI RIVER FLOODPLAIN FROM RIVER MILE (RM) 670 SOUTH OF DECATUR, NEBRASKA TO RM 0 AT ST. LOUIS, MISSOURI Prepared For: U. S. Fish and Wildlife Service Region 3 Refuges and Wildlife Minneapolis, Minnesota By: Mickey E. Heitmeyer Greenbrier Wetland Services Advance, MO 63730 Joseph L. Bartletti Prairie Engineers of Illinois, P.C. Springfield, IL 62703 And Josh D. Eash U.S. Fish and Wildlife Service, Region 3 Water Resources Branch Bloomington, MN 55437 Greenbrier Wetland Services Report No. 15-02 December 2015 Mickey E. Heitmeyer, PhD Greenbrier Wetland Services Route 2, Box 2735 Advance, MO 63730 www.GreenbrierWetland.com Publication No. 15-02 Suggested citation: Heitmeyer, M. E., J. L. Bartletti, and J. D. Eash. 2015. Hydrogeomorphic evaluation of ecosystem restoration options for the Missouri River Flood- plain from River Mile (RM) 670 south of Decatur, Nebraska to RM 0 at St. Louis, Missouri. Prepared for U. S. Fish and Wildlife Service Region 3, Min- neapolis, MN. Greenbrier Wetland Services Report 15-02, Blue Heron Conservation Design and Print- ing LLC, Bloomfield, MO. Photo credits: USACE; http://statehistoricalsocietyofmissouri.org/; Karen Kyle; USFWS http://digitalmedia.fws.gov/cdm/; Cary Aloia This publication printed on recycled paper by ii Contents EXECUTIVE SUMMARY .................................................................................... -
Chapter 5 Groundwater Quality and Hydrodynamics of an Acid Sulfate Soil Backswamp
Chapter 5 Groundwater Quality and Hydrodynamics of an Acid Sulfate Soil Backswamp 5.1 Introduction Intensive drainage of coastal floodplains has been the main factor contributing to the oxidation of acid sulfate soils (ASS) (Indraratna, Blunden & Nethery 1999; Sammut, White & Melville 1996). Drainage of backswamps removes surface water, thereby increasing the effect of evapotranspiration on watertable drawdown (Blunden & Indraratna 2000) and transportation of acidic salts to the soil surface through capillary action (Lin, Melville & Hafer 1995; Rosicky et al. 2006). During high rainfall events the oxidation products (i.e. metals and acid) are mobilised into the groundwater, and acid salts at the sediment surface are dissolved directly into the surface water (Green et al. 2006). The high efficiency of drains readily transports the acidic groundwater and surface water into the estuary and can have a detrimental impact on downstream habitats (Cook et al. 2000). The quality of water discharged from a degraded ASS wetland is controlled by the water balance, which over a given time period is: P + I + Li = E + Lo + D + S (Equation 5.1) where P is precipitation, I is irrigation, Li is the lateral inflow of water, E is evapotranspiration, Lo is surface and subsurface lateral outflow of water, D is the drainage to the watertable and S is the change in soil moisture storage above the watertable (Indraratna, Tularam & Blunden 2001; Sammut, White & Melville 1996; White et al. 1997). While this equation may give a general overview of sulfidic floodplain hydrology, an understanding of site-specific details is required for effective remediation and management of degraded ASS wetlands. -
Plant Succession on Burned Areas in Okefenokee Swamp Following the Fires of 1954 and 1955 EUGENE CYPERT Okefenokee National Wildlife Refuge U.S
Plant Succession on Burned Areas in Okefenokee Swamp Following the Fires of 1954 and 1955 EUGENE CYPERT Okefenokee National Wildlife Refuge U.S. Bureau of Sport Fisheries and 'Wildlife Waycross, GA 31501 INTRODUCTION IN 1954 and 1955, during an extreme drought, five major fires occurred in Okefenokee Swamp. These fires swept over approximately 318,000 acres of the swamp and 140,000 acres of the adjacent upland. In some areas in the swamp, the burning was severe enough to kill most of the timber and the understory vegetation and burn out pockets in the peat bed. Burns of this severity were usually small and spotty. Over most of the swamp, the burns were surface fires which generally killed most of the underbrush but rarely burned deep enough into the peat bed to kill the larger trees. In many places the swamp fires swept over lightly, burning surface duff and killing only the smaller underbrush. Some areas were missed entirely. On the upland adjacent to the swamp, the fires were very de structive, killing most of the pine timber on the 140,000 acres burned over. The destruction of pine forests on the upland and the severe 199 EUGENE CYPERT burns in the swamp caused considerable concern among conservation ists and neighboring land owners. It was believed desirable to learn something of the succession of vegetation on some of the more severely burned areas. Such knowl edge would add to an understanding of the ecology and history of the swamp and to an understanding of the relation that fires may have to swamp wildlife. -
Cypress Creek National Wildlife Refuge, Illinois
Hydrogeomorphic Evaluation of Ecosystem Restoration Options for Cypress Creek National Wildlife Refuge, Illinois Prepared For: U. S. Fish and Wildlife Service Division of Refuges, Region 3 Minneapolis, Minnesota Greenbrier Wetland Services Report 12-05 Mickey E. Heitmeyer Karen E. Mangan July 2012 HYDROGEOMORPHIC EVALUATION OF ECOSYSTEM RESTORATION OPTIONS FOR CYPRESS CREEK NATIONAL WILDLIFE REFUGE, ILLINOIS Prepared For: U.S. Fish and Wildlife Service National Wildlife Refuge System, Region 3 Minneapolis, MN and Cypress Creek National Wildlife Refuge Ullin, IL By: Mickey E. Heitmeyer, PhD Greenbrier Wetland Services Rt. 2, Box 2735 Advance, MO 63730 and Karen E. Mangan U.S. Fish and Wildlife Service Cypress Creek National Wildlife Refuge 0137 Rustic Campus Drive Ullin, IL 62992 Greenbrier Wetland Services Report 12-05 July 2012 Mickey E Heitmeyer, PhD Greenbrier Wetland Services Route 2, box 2735 Advance, MO. 63730 Publication No. 12-05 Suggested citation: Heitmeyer, M. E., K. E. Mangan. 2012. Hy- drogeomorphic evaluation of ecosystem restora- tion and management options for Cypress Creek National Wildlife Refuge,Ullin Il.. Prepared for U. S. Fish and Wildlife Service, Region 3, Minne- apolis, MN and Cypress Creek National Wildlife Refuge,Ullin,Il. Greenbrier Wetland Services Report 12-05, Blue Heron Conservation Design and Printing LLC, Bloomfield, MO. Photo credits: COVER: Limekiln Slough by Michael Jeffords Michael Jeffords, Jan Sundberg, Cary Aloia (Gardners- Gallery.com), Karen Kyle This publication printed on recycled paper by ii -
Floodplain Geomorphic Processes and Environmental Impacts of Human Alteration Along Coastal Plain Rivers, Usa
WETLANDS, Vol. 29, No. 2, June 2009, pp. 413–429 ’ 2009, The Society of Wetland Scientists FLOODPLAIN GEOMORPHIC PROCESSES AND ENVIRONMENTAL IMPACTS OF HUMAN ALTERATION ALONG COASTAL PLAIN RIVERS, USA Cliff R. Hupp1, Aaron R. Pierce2, and Gregory B. Noe1 1U.S. Geological Survey 430 National Center, Reston, Virginia, USA 20192 E-mail: [email protected] 2Department of Biological Sciences, Nicholls State University Thibodaux, Louisiana, USA 70310 Abstract: Human alterations along stream channels and within catchments have affected fluvial geomorphic processes worldwide. Typically these alterations reduce the ecosystem services that functioning floodplains provide; in this paper we are concerned with the sediment and associated material trapping service. Similarly, these alterations may negatively impact the natural ecology of floodplains through reductions in suitable habitats, biodiversity, and nutrient cycling. Dams, stream channelization, and levee/canal construction are common human alterations along Coastal Plain fluvial systems. We use three case studies to illustrate these alterations and their impacts on floodplain geomorphic and ecological processes. They include: 1) dams along the lower Roanoke River, North Carolina, 2) stream channelization in west Tennessee, and 3) multiple impacts including canal and artificial levee construction in the central Atchafalaya Basin, Louisiana. Human alterations typically shift affected streams away from natural dynamic equilibrium where net sediment deposition is, approximately, in balance with net -
* This Is an Excerpt from Protected Animals of Georgia Published By
Common Name: BLACKBANDED SUNFISH Scientific Name: Enneacanthus chaetodon Other Commonly Used Names: none Previously Used Scientific Names: none Family: Centrarchidae Rarity Ranks: G4/S1 State Legal Status: Endangered Federal Legal Status: Not Listed Description: The blackbanded sunfish is a small, laterally compressed and deep-bodied species reaching a maximum total length of 100 mm (4 inches). There is a prominent notch separating the spinous and soft-rayed portions of the dorsal fin. It is distinctively marked with 5-6 black bars along the sides that extend from the dorsum to the venter. The first of these bars passes through the eye, and the third extends through the first three membranes of the spinous dorsal fin to the upper edge of the fin. No other sunfish has this barring pattern. The blackbanded sunfish is also very colorful with black vertical bars, olive-brown to variegated-brown on the dorsum and upper sides, and orange-copper marking the leading edge of the pelvic fins and the irises. Similar Species: The small body size and distinctive color pattern make it difficult to confuse the blackbanded sunfish with any other fish species in Georgia waters. It may superficially resemble the banded (Enneacanthus obesus) and bluespotted (E. gloriosus) sunfishes, which differ in having only a shallow notch separating the spinous and soft-rayed portions of the dorsal fin and lacking the prominent dark bar extending through the anterior dorsal fin membranes. Habitat: Blackbanded sunfish are restricted to shallow, low-velocity, non-turbid waters of lakes, ponds, rivers and streams. They are strongly associated with aquatic plants, which provide habitat for foraging and cover. -
EARTH SCIENCES RESEARCH JOURNAL Development of Tropical
EARTH SCIENCES RESEARCH JOURNAL Earth Sci. Res. J. Vol. 20, No. 1 (March, 2016): O1 - O10 GEOLOGY ENGINEERING Development of Tropical Lowland Peat Forest Phasic Community Zonations in the Kota Samarahan-Asajaya area, West Sarawak, Malaysia Mohamad Tarmizi Mohamad Zulkifley1, Ng Tham Fatt1, Zainey Konjing2, Muhammad Aqeel Ashraf3,4* 1. Department of Geology, Faculty of Science, University of Malaya, Kuala Lumpur, Malaysia 2. Biostratex Sendirian Berhad, Batu Caves, Gombak, Malaysia. 3. Department of Environmental Science and Engineering, School of Environmental Studies, China University of Geosciences, 430074 Wuhan, P. R. China 4. Faculty of Science & Natural Resources, University Malaysia Sabah88400 Kota Kinabalu, Sabah, Malaysia. Corresponding authors: Muhammad Aqeel Ashraf- Faculty of Science & Natural Resources University Malaysia Sabah, 88400, Kota Kinabalu, Sabah. ([email protected]) ABSTRACT Keywords: Lowland peat swamp, Phasic community, Logging observations of auger profiles (Tarmizi, 2014) indicate a vertical, downwards, general decrease of Mangrove swamp, Riparian environment, Pollen peat humification levels with depth in a tropical lowland peat forest in the Kota Samarahan-Asajaya área in the diagram, Vegetation Succession. región of West Sarawak (Malaysia). Based on pollen analyses and field observations, the studied peat profiles can be interpreted as part of a progradation deltaic succession. Continued regression of sea levels, gave rise Record to the development of peat in a transitional mangrove to floodplain/floodbasin environment, followed by a shallow, topogenic peat depositional environment with riparian influence at approximately 2420 ± 30 years B.P. Manuscript received: 20/10/2015 (until present time). The inferred peat vegetational succession reached Phasic Community I at approximately Accepted for publication: 12/02/2016 2380 ± 30 years B.P. -
Glossary Ablation Till: Till Carried on Or Near the Surface of a Glacial Ice Column and Let Down As the Glacier Melted and Retreated
Glossary ablation till: till carried on or near the surface of a glacial ice column and let down as the glacier melted and retreated. alluvium: any mineral or detrital sediment that is transported and deposited by the flowing water of a river or stream. Riverbeds, floodplains, and deltas are all made up of alluvium. backswamp: low-lying wet areas on river floodplains, located away from the active river channel. basal till: till carried in the base of a glacial ice column and deposited under the glacier. Basal till is therefore very dense and typically forms a layer that impedes drainage. biological diversity (biodiversity): the complexity of all life at all its levels of organization, including genetic variability within species, species and species interac- tions, ecological processes, and the distribution of species and natural communities across the landscape. bog: an acidic, peat-accumulating wetland that is isolated from mineral-rich water sources by deep peat accumulation and therefore receives most of its water and nutri- ents from precipitation. Bogs are dominated by sphagnum moss and heath family shrubs. boreal forest: a circumpolar band of northern forests bordered to the north by open tundra and to the south by more transitional forests. Boreal forests are characterized by species of pine, spruce, fir, tamarack, birch, and poplar that are adapted to the extreme cold of this region. bryophyte: a division of plants including the mosses, liverworts, and hornworts. calciphile: a plant that thrives in calcium-rich soils. circumneutral: having a pH near 7.0 and therefore neither strongly acidic nor basic. cliff: an exposed, steep face of rock. -
Fish Consumption Guidelines: Rivers & Creeks
FRESHWATER FISH CONSUMPTION GUIDELINES: RIVERS & CREEKS NO RESTRICTIONS ONE MEAL PER WEEK ONE MEAL PER MONTH DO NOT EAT NO DATA Bass, LargemouthBass, Other Bass, Shoal Bass, Spotted Bass, Striped Bass, White Bass, Bluegill Bowfin Buffalo Bullhead Carp Catfish, Blue Catfish, Channel Catfish,Flathead Catfish, White Crappie StripedMullet, Perch, Yellow Chain Pickerel, Redbreast Redhorse Redear Sucker Green Sunfish, Sunfish, Other Brown Trout, Rainbow Trout, Alapaha River Alapahoochee River Allatoona Crk. (Cobb Co.) Altamaha River Altamaha River (below US Route 25) Apalachee River Beaver Crk. (Taylor Co.) Brier Crk. (Burke Co.) Canoochee River (Hwy 192 to Lotts Crk.) Canoochee River (Lotts Crk. to Ogeechee River) Casey Canal Chattahoochee River (Helen to Lk. Lanier) (Buford Dam to Morgan Falls Dam) (Morgan Falls Dam to Peachtree Crk.) * (Peachtree Crk. to Pea Crk.) * (Pea Crk. to West Point Lk., below Franklin) * (West Point dam to I-85) (Oliver Dam to Upatoi Crk.) Chattooga River (NE Georgia, Rabun County) Chestatee River (below Tesnatee Riv.) Chickamauga Crk. (West) Cohulla Crk. (Whitfield Co.) Conasauga River (below Stateline) <18" Coosa River <20" 18 –32" (River Mile Zero to Hwy 100, Floyd Co.) ≥20" >32" <18" Coosa River <20" 18 –32" (Hwy 100 to Stateline, Floyd Co.) ≥20" >32" Coosa River (Coosa, Etowah below <20" Thompson-Weinman dam, Oostanaula) ≥20" Coosawattee River (below Carters) Etowah River (Dawson Co.) Etowah River (above Lake Allatoona) Etowah River (below Lake Allatoona dam) Flint River (Spalding/Fayette Cos.) Flint River (Meriwether/Upson/Pike Cos.) Flint River (Taylor Co.) Flint River (Macon/Dooly/Worth/Lee Cos.) <16" Flint River (Dougherty/Baker Mitchell Cos.) 16–30" >30" Gum Crk. -
Okefenokee Swamp Hydrology
OKEFENOKEE SWAMP HYDROLOGY Cynthia S. Loftin' AUTHOR: 'Graduate Research Assistant-Ph.D. Candidate, USGS-BRD Florida Cooperative Fish and Wildlife Research Unit, Department of Wildlife Ecology and Conservation, University of Florida, Gainesville, Florida 32611-0450. REFERENCE: Proceedings of the 1997 Georgia Water Resources Conference, held 20-22 March 1997, at the University of Georgia, Kathryn J. Hatcher, Editor, Institute of Ecology, The University of Georgia, Athens, Georgia. Abstract. The Okefenokee Swamp is one of North topographic relief is minimal The swamp is a bowl-like America's largest freshwater wetlands. Swamp hydrology depression in the landscape with the trend in ground surface is largely controlled by precipitation and elevation from 38.4 m at Kingfisher Landing in the evapotranspiration; regional topographic features of the Northeast to 33.0 m in the area where the Suwannee River swamp control surface water movements. Manipulations to exits the swamp in the West to 34.75 m at Ellicott's Mound the swamp topography and vegetation communities during in the Southeast near the St. Mary's River outflow. Within this century have affected water movement and variability the swamp are regional topographic highs on large sand- in parts of the swamp. Changes in swamp hydrology since based islands and lows in large prairies. The prairies also the construction of the Suwannee River Sill are generally contain local topographic highs on peat-based islands that restricted to the West Central area bounded by the Pocket, may rise a meter above the surrounding inundated peat Billy's Island, Craven's Island, Minnie's Island, and surface. -
Quick Reference Fact Sheet
Okefenokee at a Glance The Okefenokee Swamp is located in Ware, Charlton, and Clinch Counties, Georgia and Baker County, Florida. Okefenokee National Wildlife Refuge was established by Executive Order in 1936. The Okefenokee Swamp covers 438,000 acres. It is 38 miles in length at its longest point by 25 miles in width at its widest point. The swamp is approximately 700 square miles. The Okefenokee National Wildlife Refuge is over 402,000 acres. The wilderness area consists of 353,981 acres and was created by the Okefenokee Wilderness Act of 1974 which is part of the Wilderness Preservation System. Okefenokee National Wildlife Refuge is the largest National Wildlife Refuge in the eastern United States. It is administered by the U.S. Fish and Wildlife Service which is under the Department of the Interior. The Okefenokee Swamp is approximately 7000 years old. It is a vast peat-filled bog inside a huge, saucer-shaped depression that was once part of the ocean floor. The elevation of the swamp varies. There is a 25 foot drop from the northwest side to the southwest side. The range in elevation is from 128 feet above sea level on the northeast side to 103 feet on the southwest side. The vegetative indicator of the natural swamp line is the presence of the saw palmetto. The Suwannee River is the principle outlet of the swamp. The Suwannee flows from the west side of the swamp and empties into the Gulf of Mexico near Cedar Key, Florida. The Suwannee River is 280 miles long. A small area of the southeastern part of the swamp is drained by the St.