Cypress--Gum Swamp (Blackwater Subtype)
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Shrub Swamp State Rank: S5 - Secure
Shrub Swamp State Rank: S5 - Secure cover of tall shrubs with Shrub Swamp Communities are a well decomposed organic common and variable type of wetlands soils. If highbush occurring on seasonally or temporarily blueberries are dominant flooded soils; They are often found in the transition zone between emergent the community is likely to marshes and swamp forests; be a Highbush Blueberry Thicket, often occurring on stunted trees. The herbaceous layer of peat. Acidic Shrub Fens are shrub swamps is often sparse and species- peatlands, dominated by poor. A mixture of species might typically low growing shrubs, along include cinnamon, sensitive, royal, or with sphagnum moss and marsh fern, common arrowhead, skunk herbaceous species of Shrub Swamp along shoreline. Photo: Patricia cabbage, sedges, bluejoint grass, bur-reed, varying abundance. Deep Serrentino, Consulting Wildlife Ecologist. swamp candles, clearweed, and Emergent Marshes and Description: Wetland shrubs dominate turtlehead. Invasive species include reed Shallow Emergent Marshes Cottontail, have easy access to the shrubs Shrub Swamps. Shrub height may be from canary grass, glossy alder-buckthorn, are graminoid dominated wetlands with and protection in the dense thickets. The <1m to 5 meters, of uniform height or common buckthorn, and purple <25% cover of tall shrubs. Acidic larvae of many rare and common moth mixed. Shrub density can be variable, loosestrife. Pondshore/Lakeshore Communities are species feed on a variety of shrubs and from dense (>75% cover) to fairly open broadly defined, variable shorelines associated herbaceous plants in shrub (25-75% cover) with graminoid, around open water. Shorelines often swamps throughout Massachusetts. herbaceous, or open water areas between merge into swamps or marshes. -
Maritime Swamp Forest (Typic Subtype)
MARITIME SWAMP FOREST (TYPIC SUBTYPE) Concept: Maritime Swamp Forests are wetland forests of barrier islands and comparable coastal spits and back-barrier islands, dominated by tall trees of various species. The Typic Subtype includes most examples, which are not dominated by Acer, Nyssa, or Fraxinus, not by Taxodium distichum. Canopy dominants are quite variable among the few examples. Distinguishing Features: Maritime Shrub Swamps are distinguished from other barrier island wetlands by dominance by tree species of (at least potentially) large stature. The Typic Subtype is dominated by combinations of Nyssa, Fraxinus, Liquidambar, Acer, or Quercus nigra, rather than by Taxodium or Salix. Maritime Shrub Swamps are dominated by tall shrubs or small trees, particularly Salix, Persea, or wetland Cornus. Some portions of Maritime Evergreen Forest are marginally wet, but such areas are distinguished by the characteristic canopy dominants of that type, such as Quercus virginiana, Quercus hemisphaerica, or Pinus taeda. The lower strata also are distinctive, with wetland species occurring in Maritime Swamp Forest; however, some species, such as Morella cerifera, may occur in both. Synonyms: Acer rubrum - Nyssa biflora - (Liquidambar styraciflua, Fraxinus sp.) Maritime Swamp Forest (CEGL004082). Ecological Systems: Central Atlantic Coastal Plain Maritime Forest (CES203.261). Sites: Maritime Swamp Forests occur on barrier islands and comparable spits, in well-protected dune swales, edges of dune ridges, and on flats adjacent to freshwater sounds. Soils: Soils are wet sands or mucky sands, most often mapped as Duckston (Typic Psammaquent) or Conaby (Histic Humaquept). Hydrology: Most Maritime Swamp Forests have shallow seasonal standing water and nearly permanently saturated soils. Some may rarely be flooded by salt water during severe storms, but areas that are severely or repeatedly flooded do not recover to swamp forest. -
The Mississippi River Delta Basin and Why We Are Failing to Save Its Wetlands
University of New Orleans ScholarWorks@UNO University of New Orleans Theses and Dissertations Dissertations and Theses 8-8-2007 The Mississippi River Delta Basin and Why We are Failing to Save its Wetlands Lon Boudreaux Jr. University of New Orleans Follow this and additional works at: https://scholarworks.uno.edu/td Recommended Citation Boudreaux, Lon Jr., "The Mississippi River Delta Basin and Why We are Failing to Save its Wetlands" (2007). University of New Orleans Theses and Dissertations. 564. https://scholarworks.uno.edu/td/564 This Thesis is protected by copyright and/or related rights. It has been brought to you by ScholarWorks@UNO 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 need to 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 University of New Orleans Theses and Dissertations by an authorized administrator of ScholarWorks@UNO. For more information, please contact [email protected]. The Mississippi River Delta Basin and Why We Are Failing to Save Its Wetlands A Thesis Submitted to the Graduate Faculty of the University of New Orleans in partial fulfillment of the requirements for the degree of Master of Science in Urban Studies By Lon J. Boudreaux Jr. B.S. Our Lady of Holy Cross College, 1992 M.S. University of New Orleans, 2007 August, 2007 Table of Contents Abstract............................................................................................................................. -
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. -
Rapids Lake, Louisville Swamp, And
U.S. Fish & Wildlife Service Forest Trail 0.6 mile loop urban influences. The Carver Rapids Unit, part of Parking Leaving from the asphalt trail below the Rapids the MN Valley State Recreation Area (DNR), is Chaska Unit Minnesota Valley Lake Education and Visitor Center, this mostly level located entirely within the Louisville Swamp Unit. Chaska Athletic Park (City of Chaska) trail courses through oak and hickory forest, with a See regulations issued by the DNR for this location. 725 W 1st St, Chaska, MN 55318 National Wildlife Refuge brief view of a slough connecting to Long Lake. View wood ducks in the slough and listen for frogs calling. Trail Descriptions Carver Riverside Park (City of Carver) State Trail Access 1.0 mi, one way 300 E Main St, Carver, MN 55315 North Hunter Lot Trail 1 mile, one way This straight, level trail goes 1 mile to a junction with Chaska, Rapids Lake & This trail is a mowed service road running from the the MN Valley State Trail to the north. Continue Bluff Park (City of Carver) parking lot on CR11 (Jonathan Carver Pkwy) to the west on the State Access Trail to join the Mazomani 102 Carver Bluffs Parkway, Carver, MN 55315 Louisville Swamp Units northeast, where it ends at the refuge boundary. Trail to the south and loop back to the parking area View native wildflowers, bur oaks, woodpeckers, and at W 145 St. Rapids Lake Unit Trail Map prairie skink in this restored oak savanna. Jonathan Carver Parkway North Hunter Lot MN Valley State Trail (DNR) 5.0 mi, one way 14905 Jonathan Carver Parkway/CR 11, Carver, MN Carver Creek Loop Trail 1.6 miles (loop) From north to south through the refuge, the trail 55315 This trail system has three entry points: Bluff Park, passes the State Access Trail then drops to cross a About the Chaska Unit Ash Street (downtown Carver), and the Rapids Lake bridge over Sand Creek. -
U.S. National Vegetation Classification: Advancing The
U.S. National Vegetation Classification: Advancing the Description and Management of the Nation’s Ecosystems Use of the NVC hierarchy to scale the GAP/LANDFIRE National Ecosystems Map Legend Don Long (U.S. Forest Service), Anne Davidson (GAP, BSU) Todd Earnhardt (GAP , NSCU) Alexa McKerrow (U.S. Geological Survey) . Background Methods Results A national inventory of the existing vegetation across the There are 551 natural vegetation classes represented in the 6 Classes 13 Subclasses 22 Formations U.S. has been central to the missions of both the GAP/LANDFIRE National Terrestrial Ecosystems Map for the a Landscape Fire and Resource Management Planning Tools conterminous U.S. The crosswalk allows for the Project (LANDFIRE) and the National Gap Analysis Program aggregation of the mapped classes into the hierarchical b (GAP). Over the past several years these two programs structure of the USNVC; specifically, the ecological systems a. Forest & Woodland a. Temperate & Boreal Forest & Woodland a. Temperate Flooded & Swamp Forest b. Desert & Semi-Desert b. Warm Desert & Semi-Desert Woodland, b. Warm Desert & Semi-Desert Scrub & have come together to collaborate on the next generation are crosswalked to the middle and upper levels of the Scrub & Grassland Grassland highly detailed existing vegetation maps for the U.S. This USNVC. Relationships between the two classification 51 Divisions 112 Macrogroups 240 Groups collaboration leverages the mapping and inventory to systems developed by NatureServe ecologists were used to meet needs for both fire and fuels management, as well link the mapped Ecological Systems to the Group level of as for wildlife habitat conservation planning. the USNVC. -
Lafayette Creek Property—Phases I and Ii Umbrella
LAFAYETTE CREEK PROPERTY—PHASES I AND II UMBRELLA REGIONAL MITIGATION PLANS FOR FLORIDA DEPARTMENT OF TRANSPORTATION PROJECTS CONCEPTUAL MITIGATION PLAN WALTON COUNTY, FLORIDA June 20, 2011 Prepared for: Mr. David Clayton Northwest Florida Water Management District 81 Water Management Drive Havana, FL 32333 Prepared by: ________________________________ ________________________________ Caitlin E. Elam Richard W. Cantrell Staff Scientist Senior Consultant 4240-034 Y100 Lafayette Creek Phases I and II Restoration Plan 062011_E.doc Lafayette Creek Property—Phases I and II Umbrella Regional Mitigation Plans for Florida Department of Transportation Projects June 20, 2011 TABLE OF CONTENTS 1.0 PROJECT OVERVIEW AND GOALS ............................................................................. 1 2.0 LOCATION AND LANDSCAPE ...................................................................................... 2 3.0 EXISTING CONDITIONS ................................................................................................. 2 4.0 LISTED SPECIES ............................................................................................................ 13 5.0 EXOTIC SPECIES ............................................................................................................ 17 6.0 HISTORIC CONDITIONS ............................................................................................... 17 7.0 SOILS ............................................................................................................................... -
Exploring Our Wonderful Wetlands Publication
Exploring Our Wonderful Wetlands Student Publication Grades 4–7 Dear Wetland Students: Are you ready to explore our wonderful wetlands? We hope so! To help you learn about several types of wetlands in our area, we are taking you on a series of explorations. As you move through the publication, be sure to test your wetland wit and write about wetlands before moving on to the next exploration. By exploring our wonderful wetlands, we hope that you will appreciate where you live and encourage others to help protect our precious natural resources. Let’s begin our exploration now! Southwest Florida Water Management District Exploring Our Wonderful Wetlands Exploration 1 Wading Into Our Wetlands ................................................Page 3 Exploration 2 Searching Our Saltwater Wetlands .................................Page 5 Exploration 3 Finding Out About Our Freshwater Wetlands .............Page 7 Exploration 4 Discovering What Wetlands Do .................................... Page 10 Exploration 5 Becoming Protectors of Our Wetlands ........................Page 14 Wetlands Activities .............................................................Page 17 Websites ................................................................................Page 20 Visit the Southwest Florida Water Management District’s website at WaterMatters.org. Exploration 1 Wading Into Our Wetlands What exactly is a wetland? The scientific and legal definitions of wetlands differ. In 1984, when the Florida Legislature passed a Wetlands Protection Act, they decided to use a plant list containing plants usually found in wetlands. We are very fortunate to have a lot of wetlands in Florida. In fact, Florida has the third largest wetland acreage in the United States. The term wetlands includes a wide variety of aquatic habitats. Wetland ecosystems include swamps, marshes, wet meadows, bogs and fens. Essentially, wetlands are transitional areas between dry uplands and aquatic systems such as lakes, rivers or oceans. -
Peat Swamp and Lowland Forests of Sumatra (Indonesia)
Forest Area Key Facts & Peat Swamp and Lowland Carbon Emissions Forests of Sumatra (Indonesia) from Deforestation Forest location and brief description With an area of some 470,000 km2, Sumatra is Indonesia’s largest island, and the world’s sixth largest, supporting 40 million people. The lowland forests cover approximately 118,300 km2 of the eastern part of the island. These rainforests are characterized by large, buttressed trees dominated by the Dipterocarpaceae family, woody climbers and epiphytes. Figs are also common in the lowland forests. There are more than 100 fig species in Sumatra. According to the SPOT Vegetation 2006 data, the Sumatran peat swamp forests total approximately 33,600 km2. These forests are located on Sumatra’s eastern coast and boast the deepest peat in Indonesia. Over 30 per cent of Sumatra’s peat are over 4 metres deep. Most of the peat are in the Sumatran province of Riau (56.1 per cent of its total provincial area). Unique qualities of forest area Sumatra’s lowland forests are home to a range of species including: Sumatran pine, Rafflesia arnoldii (the world’s largest individual flower, measuring up to 1 metre wide), Amorphophallus spp. (world’s tallest and largest inflorescence flower measuring up to 2 metres tall), Sumatran tiger, orang utan, Sumatran rhinoceros, Sumatran elephant, Malayan tapir, Malayan sun bear, Bornean clouded leopard, and many birds and butterflies. Although Sumatra’s peat swamp forests do not support an abundant terrestrial wildlife, they do support some of the island’s biggest and • The forest sector accounts rarest animals, such as the critically endangered Sumatran tiger, and the for 85 per cent of Indonesia’s endangered Sumatran rhinoceros and Asian elephant. -
Mcgovern Pond Dredging and Restoration Project Spicebush Swamp Park – 173 Mountain Road, West Hartford, CT
McGovern Pond Dredging and Restoration Project Spicebush Swamp Park – 173 Mountain Road, West Hartford, CT History: Established in 1962, Spicebush Swamp Park was West Hartford’s first park to be set aside as a natural area for nature study or walking, and as a 33-acre, outdoor classroom for schools to use. McGovern Pond was created in the park by excavating an area of approximately one acre in Spicebush Swamp Park around 1968. The pond is maintained by a flow of water from a branch of the Trout Brook. Since its creation, McGovern pond has slowly been filled with sediments washed in from upstream watershed sources. These sediments, which consist primarily of road sand, eroded soils from construction sites and organic plant materials, have filled in approximately one quarter of the upstream side of the pond to an average depth of only 1 foot. This process is referred to as “cultural” eutrophication and is a common occurrence in heavily developed watersheds. As the eutrophication process advances, the ability of the affected pond to support a diverse aquatic community diminishes. Sediment at McGovern Pond was addressed once, approximately 15 years ago, when Public Works established a sediment trap, but they did not dredge the pond or address organic matter that had built up around the pond edges. Reasons for Project – Habitat restoration and Environmental Education: In a letter from 2006, Don Mysling, a Senior Fisheries Biologist with the CT DEEP, recommended that pond restoration projects for this area of Connecticut should be planned to provide habitat for warm water fish species such a largemouth bass and sunfish. -
Mississippi River Reintroduction Into Maurepas Swamp - Planning Cost: Category 1: $14,190,000 Responsible Council Member: State of Louisiana
Gulf Coast Mississippi River Delta Watershed Ecosystem Restoration Mississippi River Reintroduction into the Maurepas Swamp Council (LA_RESTORE_005_000_Cat1) Project Name: Mississippi River Reintroduction into Maurepas Swamp - Planning Cost: Category 1: $14,190,000 Responsible Council Member: State of Louisiana Project Details: The Maurepas Swamp is one of the largest areas of forested wetlands along the Gulf Coast, encompassing approximately 57,000 hectares (approximately 140,850 acres) of bald cypress-tupelo swamp west of Lake Pontchartrain. Historically, the swamp received sediment and nutrient inputs from the Mississippi River during seasonal overbank flooding; however, reduced freshwater inflow and sediment input has caused land loss within the sub-basin and resulted in the periodic introduction of brackish water from Lake Pontchartrain into Lake Maurepas and the swamp. Activities: The project would include engineering and design of the Mississippi River Reintroduction into Maurepas Swamp project, leading to construction-ready plans and specifications and the development of an adaptive management plan to guide decision-making for future project maintenance activities. If implemented in the future, the project would consist of the following major components designed to divert fresh water from the river into the Maurepas Swamp: a gated river intake structure; a box culvert through the levee; a sedimentation basin; a conveyance channel; and a drainage pump station. The maximum design flow is 2,000 cubic feet per second. Environmental Benefits: If implemented in the future, in addition to restoring and enhancing a total of 18,300 hectares (approximately 45,220 acres) of forested wetland, the project would provide a host of other benefits to wildlife that are dependent on cypress-tupelo swamps. -
Natural Vegetation of the Carolinas: Classification and Description of Plant Communities of the Lumber (Little Pee Dee) and Waccamaw Rivers
Natural vegetation of the Carolinas: Classification and Description of Plant Communities of the Lumber (Little Pee Dee) and Waccamaw Rivers A report prepared for the Ecosystem Enhancement Program, North Carolina Department of Environment and Natural Resources in partial fulfillments of contract D07042. By M. Forbes Boyle, Robert K. Peet, Thomas R. Wentworth, Michael P. Schafale, and Michael Lee Carolina Vegetation Survey Curriculum in Ecology, CB#3275 University of North Carolina Chapel Hill, NC 27599‐3275 Version 1. May 19, 2009 1 INTRODUCTION The riverine and associated vegetation of the Waccamaw, Lumber, and Little Pee Rivers of North and South Carolina are ecologically significant and floristically unique components of the southeastern Atlantic Coastal Plain. Stretching from northern Scotland County, NC to western Brunswick County, NC, the Lumber and northern Waccamaw Rivers influence a vast amount of landscape in the southeastern corner of NC. Not far south across the interstate border, the Lumber River meets the Little Pee Dee River, influencing a large portion of western Horry County and southern Marion County, SC before flowing into the Great Pee Dee River. The Waccamaw River, an oddity among Atlantic Coastal Plain rivers in that its significant flow direction is southwest rather that southeast, influences a significant portion of the eastern Horry and eastern Georgetown Counties, SC before draining into Winyah Bay along with the Great Pee Dee and several other SC blackwater rivers. The Waccamaw River originates from Lake Waccamaw in Columbus County, NC and flows ~225 km parallel to the ocean before abrubtly turning southeast in Georgetown County, SC and dumping into Winyah Bay.