Upland Shores

Total Page:16

File Type:pdf, Size:1020Kb

Upland Shores Upland Shores Rivershores ctober, 1927, was a wet month in Vermont. Rainfall had been higher than usual. The ground was saturated, and rivers and streams were full. On the first Oday of November, an unusual series of meteorological events began to converge on Vermont. By November 3, rain was falling in unprecedented amounts, and by the end of the day on the 4th, nine inches had fallen in some parts of the state. The already full streams and wet ground could not handle all this water, and the result was the greatest natural disaster in Vermont’s written history: the Great Flood of 1927. Curiously, New Englanders from outside Vermont’s borders do not count the 1927 flood as a major event. There was some damage in neighboring states, but the bulk of the rainfall, and most of the damage, occurred in Vermont. Eighty-four Vermonters lost their lives, 55 of them in the Winooski Valley alone. River towns throughout Vermont keep the history of the Great Flood alive. City Hall in Montpelier, on the Winooski River, is decorated with photographs of water lapping the steps of the Capitol. A marker in Cambridge, on the Lamoille River, shows that the floodwaters reached the second stories of buildings in the village. Gaysville, on the White River, was washed away completely and is remembered only in pictures. The loss of human life and property caused by the flood of 1927 and lesser floods is well documented. Changes to the natural communities of rivershores and floodplains are not as well understood, however. How did the plants and animals of the rivershores respond to so much water? Local lore in the town of Sharon, on the White River, tells us that a huge amount of floodplain land was lost in the 1927 flood. Large areas of open ledge on the riverbank are said to have been laid bare. A 60 acre field became a 40 acre field in two dramatic days. Rivershores, perhaps more than any other natural system, reflect the impacts of short- term events. A flood may, in a few short hours, remove tons of soil that took thousands of years to accumulate. An ice jam in the winter may kill trees and shrubs. Spring floods may leave silt carried from far upstream, covering plants and rock. The natural tendency of a river is to clear anything in its path, either by the sheer force of moving water or, in cold climates, by the more abrasive force of ice. When the waters recede and the ice disappears – that is, for most of the growing season – rivershores are calm, sunny, open places, naturally stripped of trees and shrubs. The only perennial plants that survive the regular abrasion and flooding are the ones with firm roots or rhizomes that hold them tenaciously in place. Annuals survive by sending their progeny out to unknown seed beds downstream. 190 / Wetland, Woodland, Wildland Rivershore plants may deceive the naturalist in summer: long, lacy grasses wave in the breeze, delicate harebell flowers hang from slender stalks, and translu- cent touch-me-not leaves grace waist-high plants. But visit the same riverbank in flood time, and you’ll find the grasses flattened to the ground, harebells reduced to tiny basal parts that hang on in cracks in the rock, and the touch-me-nots long gone, having dispersed their seeds in late summer. Rivershores are dynamic places, and because of the severity of the natural forces acting on them, they are unique in the largely forested northeast. Two rivershore types are described here: Riverside Outcrop and Erosional River Bluff. Five other rivershore communities are technically wetlands. Like many rivers flowing out of the mountains, the Huntington River responds quickly to heavy rainfall and melting snow and has a floodplain that changes frequently. Lakeshores The natural communities that inhabit the shores of our lakes and ponds are as varied as the lakes and ponds themselves. No two are alike. Many lakeshore communities are wet for much of the growing season and are therefore classified as wetlands. On many lakes and ponds, there is practically nothing that can be called shore; forest meets lake abruptly, with no fanfare. It is only where there is something to challenge the forest that one finds open, dry shoreline communities on a lake. Ice challenges the forest by pushing upward onto the shore as a lake freezes, scarring the bark of trees and shrubs, and ultimately killing them. Water challenges the forest in lakes where spring flooding lasts long enough to drown trees. Wind challenges the forest by stressing trees, or by depositing sand and moving it about year after year, as on a beach or dune. We recognize three dry, open communities of lakeshores: Lake Shale or Cobble Beach, Lake Sand Beach, and Sand Dune. Spruce-Fir Northern Hardwood ForestUpland Formation Shores / 191 HOW TO IDENTIFY Upland Shore Natural Communities Read the short descriptions that follow and choose the community that fits best. Then go to the page indicated to confirm your decision. Riverside Outcrop: These are bedrock exposures along rivers and streams, where flooding and ice scour combine with summer drought to keep trees and shrubs from becoming established. Vegetation is very sparse, with plants growing in small patches of soil that accumulate in cracks. Go to page 193. Erosional River Bluff: These are steep, eroding areas of sand, gravel, clay, or silt, on riverbends where natural movement causes continued sloughing of sediments. Go to page 197. Lake Shale or Cobble Beach: These are lake beaches made of coarse fragments such as shale or cobble. They are kept open by spring flooding, ice scour, and wave action. Moisture is not abundant during the growing season, in contrast with Lakeshore Grassland, which is a wetland community. Go to page 200. Lake Sand Beach: These are lake beaches made from finer soil fragments (sand). They are kept open by spring flooding, ice scour, wave action, wind, and regular deposition of new sediments. Go to page 203. Sand Dune: These are always associated with Sand Beaches and are found land- ward of them. They are areas of sand movement due to wind. Vegetation is sparse. Go to page 206. 192 / Wetland, Woodland, Wildland RIVERSIDE OUTCROP ECOLOGY AND PHYSICAL SETTING Riverside Outcrops are places along rivers and streams where bedrock is exposed and treeless. They are most common where waters are swift, such as at narrows, gorges, rapids, and falls. The large rivers, like the Connecticut, Winooski, Lamoille, Missisquoi, and White, have the most extensive areas of Riverside Outcrops. Smaller rivers and streams, with less extensive flooding and less ice to scour banks, tend to have smaller outcrop areas. Although Riverside Outcrops are similar to outcrops that are not near water in their exposure to the heat of the sun and their lack of soil, most are distinct in that they are influenced by river processes. Where outcrops are within a few feet of river level, they are scoured regularly in the winter by ice as it expands and pushes up on the banks, and also in spring as the great floes move downstream on DISTRIBUTION/ABUNDANCE spring floods. This scouring kills most woody plants by Riverside Outcrops are damaging the growing tissue in their bark. Where outcrops found on rivers and streams are within the zone of flooding, high water deposits throughout Vermont, though they are nowhere abundant or sediments in the rock crevices, creating miniature pockets of large. They are found on all alluvial silt or silt loam, soil types that are more commonly the larger rivers, including the found in floodplain forests. These loamy pockets of soil Connecticut, White, West, tend to be nutrient-enriched and hold moisture well, in Black, Ottauquechee, Deerfield, Winooski, Lamoille, contrast to the nutrient-poor soils that develop in place on and Missisquoi, and very some other kinds of rock outcrops. And where outcrops are likely others. Communities near falls, they are bathed in mist, which provides needed with similar groups of species moisture. Valley fog gives Riverside Outcrops added are known to occur in all New England states and in New moisture, too, especially in late summer and fall. York and are likely to occur in Riverside Outcrops can be nearly level to gently sloping, adjacent Canada as well. Out- or they can be completely vertical, as in a gorge. The crop communities on rivers in steeper the slope, the more difficult the accumulation of other parts of North America and the world may rely on soil, and the sparser the vegetation tends to be. Some similar ecological process, Riverside Outcrops are formed by erosion of bedrock over but the species are different. Upland ShoresProfile / 193 RIVERSIDE OUTCROP millennia – this process creates gorges, and ANIMALS in some gorges the exposed rock can be The mammals and birds that one sees far above the present-day river. on Riverside Outcrops are probably more Any kind of rock can form the substrate a factor of the habitat that surrounds the for a Riverside Outcrop. Schists and outcrop than the outcrop itself. Small phyllites line much of the Connecticut, mammals such as river otter and mink will schists and grey limestones are common pass through, moving to or from a river. on the White, and white limestone can be Large mammals may use a riverside outcrop found on the lower Winooski. Granite is as access to water. Shorebirds can be found seen very locally, as on a short stretch of occasionally on rocky shores, though they the West River in southern Vermont and are more likely to feed on muddy shores.
Recommended publications
  • Geomorphic Classification of Rivers
    9.36 Geomorphic Classification of Rivers JM Buffington, U.S. Forest Service, Boise, ID, USA DR Montgomery, University of Washington, Seattle, WA, USA Published by Elsevier Inc. 9.36.1 Introduction 730 9.36.2 Purpose of Classification 730 9.36.3 Types of Channel Classification 731 9.36.3.1 Stream Order 731 9.36.3.2 Process Domains 732 9.36.3.3 Channel Pattern 732 9.36.3.4 Channel–Floodplain Interactions 735 9.36.3.5 Bed Material and Mobility 737 9.36.3.6 Channel Units 739 9.36.3.7 Hierarchical Classifications 739 9.36.3.8 Statistical Classifications 745 9.36.4 Use and Compatibility of Channel Classifications 745 9.36.5 The Rise and Fall of Classifications: Why Are Some Channel Classifications More Used Than Others? 747 9.36.6 Future Needs and Directions 753 9.36.6.1 Standardization and Sample Size 753 9.36.6.2 Remote Sensing 754 9.36.7 Conclusion 755 Acknowledgements 756 References 756 Appendix 762 9.36.1 Introduction 9.36.2 Purpose of Classification Over the last several decades, environmental legislation and a A basic tenet in geomorphology is that ‘form implies process.’As growing awareness of historical human disturbance to rivers such, numerous geomorphic classifications have been de- worldwide (Schumm, 1977; Collins et al., 2003; Surian and veloped for landscapes (Davis, 1899), hillslopes (Varnes, 1958), Rinaldi, 2003; Nilsson et al., 2005; Chin, 2006; Walter and and rivers (Section 9.36.3). The form–process paradigm is a Merritts, 2008) have fostered unprecedented collaboration potentially powerful tool for conducting quantitative geo- among scientists, land managers, and stakeholders to better morphic investigations.
    [Show full text]
  • 2002 Yearbook and Annual Report
    2002 Yearbook and Annual Report Teaching individuals to take personal responsibility for all of their actions -The VYCC Mission Statement A Message from the President Dear Friends, I am pleased to report that the VYCC has never been stronger. We made it work with our extraordinary staff, board members, and volunteers who are extremely talented, committed, and a lot of fun to work with. Thank you! While this is a time when we can take great pride in our accomplishments, it is not a time when we can rest, even for a minute…the needs in our communities are greater than ever and growing, and the Thomas Hark with children Eli (left), VYCC is an important part of the answer. Zachary (middle), and newborn Rosie (right). Our mission of teaching individuals to take personal responsibility for their own actions, what one says and does, is absolutely vital and essential to creating strong and healthy communities. It is these lessons learned in the Corps that will make the difference in the years and decades to come. While it is true that we operate state parks and do incredible trail and other natural resource work, and that this work all by itself makes the VYCC vital to Vermont, the true value of this organization is what individuals learn from their experiences, and then take with them and use the rest of their lives…it is the values of respect, hard work, and personal responsibility that become imbedded in an individual after a stint in the Corps. Many people think of the VYCC as that small group who built a local trail…though few realize over 350 Staff and Corps Members were enrolled in 2002 and completed over 80,000 hours of important conservation work on 800 distinct projects in every corner of Vermont.
    [Show full text]
  • Morphologic Characteristics of the Blow River Delta, Yukon Territory, Canada
    Louisiana State University LSU Digital Commons LSU Historical Dissertations and Theses Graduate School 1969 Morphologic Characteristics of the Blow River Delta, Yukon Territory, Canada. James Murl Mccloy Louisiana State University and Agricultural & Mechanical College Follow this and additional works at: https://digitalcommons.lsu.edu/gradschool_disstheses Recommended Citation Mccloy, James Murl, "Morphologic Characteristics of the Blow River Delta, Yukon Territory, Canada." (1969). LSU Historical Dissertations and Theses. 1605. https://digitalcommons.lsu.edu/gradschool_disstheses/1605 This Dissertation is brought to you for free and open access by the Graduate School at LSU Digital Commons. It has been accepted for inclusion in LSU Historical Dissertations and Theses by an authorized administrator of LSU Digital Commons. For more information, please contact [email protected]. This dissertation has been microfilmed exactly as received 70-252 McCLOY, James Murl, 1934- MORPHOLOGIC CHARACTERISTICS OF THE BLOW RIVER DELTA, YUKON TERRITORY, CANADA. The Louisiana State University and Agricultural and Mechanical College, Ph.D., 1969 Geography University Microfilms, Inc., Ann Arbor, Michigan Morphologic Characteristics of the Blow River Belta, Yukon Territory, Canada A Dissertation Submitted to the Graduate Faculty of the Louisiana State University and Agricultural and Mechanical College in partial fulfillment of the requirements for the degree of Doctor of Philosophy in The Department of Geography and Anthropology by James Murl McCloy B.A., State College at Los Angeles, 1961 May, 1969 ACKNOWLEDGEMENTS Research culminating in this dissertation was conducted under the auspices of the Arctic Institute of North America. The major portion of the financial support was received from the United States Army under contract no. BA-ARO-D-3I-I2I4.-G832, "Arctic Environmental Studies." Additional financial assistance during part of the writing stage was received in the form of a research assistantship from the Coastal Studies Institute, Louisi­ ana State University.
    [Show full text]
  • Coastal Wetland Trends in the Narragansett Bay Estuary During the 20Th Century
    u.s. Fish and Wildlife Service Co l\Ietland Trends In the Narragansett Bay Estuary During the 20th Century Coastal Wetland Trends in the Narragansett Bay Estuary During the 20th Century November 2004 A National Wetlands Inventory Cooperative Interagency Report Coastal Wetland Trends in the Narragansett Bay Estuary During the 20th Century Ralph W. Tiner1, Irene J. Huber2, Todd Nuerminger2, and Aimée L. Mandeville3 1U.S. Fish & Wildlife Service National Wetlands Inventory Program Northeast Region 300 Westgate Center Drive Hadley, MA 01035 2Natural Resources Assessment Group Department of Plant and Soil Sciences University of Massachusetts Stockbridge Hall Amherst, MA 01003 3Department of Natural Resources Science Environmental Data Center University of Rhode Island 1 Greenhouse Road, Room 105 Kingston, RI 02881 November 2004 National Wetlands Inventory Cooperative Interagency Report between U.S. Fish & Wildlife Service, University of Massachusetts-Amherst, University of Rhode Island, and Rhode Island Department of Environmental Management This report should be cited as: Tiner, R.W., I.J. Huber, T. Nuerminger, and A.L. Mandeville. 2004. Coastal Wetland Trends in the Narragansett Bay Estuary During the 20th Century. U.S. Fish and Wildlife Service, Northeast Region, Hadley, MA. In cooperation with the University of Massachusetts-Amherst and the University of Rhode Island. National Wetlands Inventory Cooperative Interagency Report. 37 pp. plus appendices. Table of Contents Page Introduction 1 Study Area 1 Methods 5 Data Compilation 5 Geospatial Database Construction and GIS Analysis 8 Results 9 Baywide 1996 Status 9 Coastal Wetlands and Waters 9 500-foot Buffer Zone 9 Baywide Trends 1951/2 to 1996 15 Coastal Wetland Trends 15 500-foot Buffer Zone Around Coastal Wetlands 15 Trends for Pilot Study Areas 25 Conclusions 35 Acknowledgments 36 References 37 Appendices A.
    [Show full text]
  • New York State Artificial Reef Plan and Generic Environmental Impact
    TABLE OF CONTENTS EXECUTIVE SUMMARY ...................... vi 1. INTRODUCTION .......................1 2. MANAGEMENT ENVIRONMENT ..................4 2.1. HISTORICAL PERSPECTIVE. ..............4 2.2. LOCATION. .....................7 2.3. NATURAL RESOURCES. .................7 2.3.1 Physical Characteristics. ..........7 2.3.2 Living Resources. ............. 11 2.4. HUMAN RESOURCES. ................. 14 2.4.1 Fisheries. ................. 14 2.4.2 Archaeological Resources. ......... 17 2.4.3 Sand and Gravel Mining. .......... 18 2.4.4 Marine Disposal of Waste. ......... 18 2.4.5 Navigation. ................ 18 2.5. ARTIFICIAL REEF RESOURCES. ............ 20 3. GOALS AND OBJECTIVES .................. 26 3.1 GOALS ....................... 26 3.2 OBJECTIVES .................... 26 4. POLICY ......................... 28 4.1 PROGRAM ADMINISTRATION .............. 28 4.1.1 Permits. .................. 29 4.1.2 Materials Donations and Acquisitions. ... 31 4.1.3 Citizen Participation. ........... 33 4.1.4 Liability. ................. 35 4.1.5 Intra/Interagency Coordination. ...... 36 4.1.6 Program Costs and Funding. ......... 38 4.1.7 Research. ................. 40 4.2 DEVELOPMENT GUIDELINES .............. 44 4.2.1 Siting. .................. 44 4.2.2 Materials. ................. 55 4.2.3 Design. .................. 63 4.3 MANAGEMENT .................... 70 4.3.1 Monitoring. ................ 70 4.3.2 Maintenance. ................ 72 4.3.3 Reefs in the Exclusive Economic Zone. ... 74 4.3.4 Special Management Concerns. ........ 76 4.3.41 Estuarine reefs. ........... 76 4.3.42 Mitigation. ............. 77 4.3.43 Fish aggregating devices. ...... 80 i 4.3.44 User group conflicts. ........ 82 4.3.45 Illegal and destructive practices. .. 85 4.4 PLAN REVIEW .................... 88 5. ACTIONS ........................ 89 5.1 ADMINISTRATION .................. 89 5.2 RESEARCH ..................... 89 5.3 DEVELOPMENT .................... 91 5.4 MANAGEMENT .................... 96 6. ENVIRONMENTAL IMPACTS ................. 97 6.1 ECOSYSTEM IMPACTS.
    [Show full text]
  • Understanding the Temporal Dynamics of the Wandering Renous River, New Brunswick, Canada
    Earth Surface Processes and Landforms EarthTemporal Surf. dynamicsProcess. Landforms of a wandering 30, 1227–1250 river (2005) 1227 Published online 23 June 2005 in Wiley InterScience (www.interscience.wiley.com). DOI: 10.1002/esp.1196 Understanding the temporal dynamics of the wandering Renous River, New Brunswick, Canada Leif M. Burge1* and Michel F. Lapointe2 1 Department of Geography and Program in Planning, University of Toronto, 100 St. George Street, Toronto, Ontario, M5S 3G3, Canada 2 Department of Geography McGill University, 805 Sherbrooke Street West, Montreal, Quebec, H3A 2K6, Canada *Correspondence to: L. M. Burge, Abstract Department of Geography and Program in Planning, University Wandering rivers are composed of individual anabranches surrounding semi-permanent of Toronto, 100 St. George St., islands, linked by single channel reaches. Wandering rivers are important because they Toronto, M5S 3G3, Canada. provide habitat complexity for aquatic organisms, including salmonids. An anabranch cycle E-mail: [email protected] model was developed from previous literature and field observations to illustrate how anabranches within the wandering pattern change from single to multiple channels and vice versa over a number of decades. The model was used to investigate the temporal dynamics of a wandering river through historical case studies and channel characteristics from field data. The wandering Renous River, New Brunswick, was mapped from aerial photographs (1945, 1965, 1983 and 1999) to determine river pattern statistics and for historical analysis of case studies. Five case studies consisting of a stable single channel, newly formed anabranches, anabranches gaining stability following creation, stable anabranches, and an abandoning anabranch were investigated in detail.
    [Show full text]
  • Appendix E Fish Habitat Utilization Literature Review
    Appendix E Fish Habitat Utilization Literature Review East Kitsap Nearshore Assessment Appendix E Appendix E - Fish Habitat Utilization Literature Review Toft et al. (2007) City Shoreline Fish Distribution Study objective: study the abundance and behavior of juvenile salmon and other fishes among various marine shoreline habitat types near the city of Seattle. Focused on 5 types of shorelines - cobble beach - sand beach - riprap extending into the upper intertidal zone - deep riprap extending into the subtidal - edge of overwater structures Also examined stomach contents of juvenile salmon. Fish sampling methods included enclosure nets and snorkel surveys. Riprap often results in greater beach slopes and steep embankments which effectively reduces the intertidal zone. These characteristics in turn, result in habitat loss for juvenile flatfishes. At high intertidal habitats, more crab were encountered at cobble beaches compared to sand beaches and riprap. Demersal fishes (cottids) were found in greater numbers at riprap. Differences in species density between habitat type were more apparent for demersal fishes than for pelagic species. Densities of salmon were significantly different among habitat types. The highest densities occurred at the edge of overwater structures and in deep riprap. Deep riprap creates some structured habitat which seems to attract surfperches and gunnels. Threespine stickleback, tubesnout, and bay pipefish were also more prevalent at deep riprap than at cobble, sand, and high elevation riprap. Beamer et al. (2006) – Habitat and fish use of pocket estuaries in the Whidbey basin and north Skagit county bays, 2004 and 2005 Pocket estuaries are characterized as having more dilute marine water relative to the surrounding estuary.
    [Show full text]
  • Southeast Region
    VT Dept. of Forests, Parks and Recreation Mud Season Trail Status List is updated weekly. Please visit www.trailfinder.info for more information. Southeast Region Trail Name Parcel Trail Status Bear Hill Trail Allis State Park Closed Amity Pond Trail Amity Pond Natural Area Closed Echo Lake Vista Trail Camp Plymouth State Park Caution Curtis Hollow Road Coolidge State Forest (east) Open Slack Hill Trail Coolidge State Park Closed CCC Trail Coolidge State Park Closed Myron Dutton Trail Dutton Pines State Park Open Sunset Trail Fort Dummer State Park Open Broad Brook Trail Fort Dummer State Park Open Sunrise Trail Fort Dummer State Park Open Kent Brook Trail Gifford Woods State Park Closed Appalachian Trail Gifford Woods State Park Closed Old Growth Interpretive Trail Gifford Woods State Park Closed West River Trail Jamaica State Park Open Overlook Trail Jamaica State Park Closed Hamilton Falls Trail Jamaica State Park Closed Lowell Lake Trail Lowell Lake State Park Closed Gated Road Molly Beattie State Forest Closed Mt. Olga Trail Molly Stark State Park Closed Weathersfield Trail Mt. Ascutney State Park Closed Windsor Trail Mt. Ascutney State Park Closed Futures Trail Mt. Ascutney State Park Closed Mt. Ascutney Parkway Mt. Ascutney State Park Open Brownsville Trail Mt. Ascutney State Park Closed Gated Roads Muckross State Park Open Healdville Trail Okemo State Forest Closed Government Road Okemo State Forest Closed Mountain Road Okemo State Forest Closed Gated Roads Proctor Piper State Forest Open Quechee Gorge Trail Quechee Gorge State Park Caution VINS Nature Center Trail Quechee Gorge State Park Open Park Roads Silver Lake State Park Open Sweet Pond Trail Sweet Pond State Park Open Thetford Academy Trail Thetford Hill State Park Closed Gated Roads Thetford Hill State Park Open Bald Mt.
    [Show full text]
  • Appendix a Places to Visit and Natural Communities to See There
    Appendix A Places to Visit and Natural Communities to See There his list of places to visit is arranged by biophysical region. Within biophysical regions, the places are listed more or less north-to-south and by county. This list T includes all the places to visit that are mentioned in the natural community profiles, plus several more to round out an exploration of each biophysical region. The list of natural communities at each site is not exhaustive; only the communities that are especially well-expressed at that site are listed. Most of the natural communities listed are easily accessible at the site, though only rarely will they be indicated on trail maps or brochures. You, the naturalist, will need to do the sleuthing to find out where they are. Use topographic maps and aerial photographs if you can get them. In a few cases you will need to do some serious bushwhacking to find the communities listed. Bring your map and compass, and enjoy! Champlain Valley Franklin County Highgate State Park, Highgate Vermont Department of Forests, Parks, and Recreation Temperate Calcareous Cliff Rock River Wildlife Management Area, Highgate Vermont Department of Fish and Wildlife Silver Maple-Sensitive Fern Riverine Floodplain Forest Alder Swamp Missisquoi River Delta, Swanton and Highgate Missisquoi National Wildlife Refuge U.S. Fish and Wildlife Service Protected with the assistance of The Nature Conservancy Silver Maple-Sensitive Fern Riverine Floodplain Forest Lakeside Floodplain Forest Red or Silver Maple-Green Ash Swamp Pitch Pine Woodland Bog
    [Show full text]
  • North Hero Map and Guide
    North Hero State Park FORESTS, PARKS & RECREATION VERMONT North Hero, Vermont AGENCY OF NATURAL RESOURCES Stephenson North Point Lake Champlain PRIVATE PRIVATE Bull Rush Point PRIVATE PROPERTY Lakeview Dr. 0 150 300 600 900 to N. Hero village feet & 2 LEGEND Staff Quarters Cartop boat launch Parking Portable toilet Swimming area Trail Picnic area Park boundary ephelps-revised 03/2019 Isle LaMotte North Hero State Park ● St. Anne’s Shrine ● Ancient coral reef Welcome to North Hero State Park. Land for North Hero this 399-acre park was purchased in 1963. North Hero Nearly one-third of the land area lies below 100 ●Knight Point State Park feet in elevation. Lake Champlain normally State Park fluctuates from about 95 to 101 feet above sea Milton level, subjecting much of the park to seasonal ● Sand Bar State Park Map & Guide inundation. The forest type in the floodplain area is uncommon in Vermont, found only around Alburgh Lake Champlain. The lakeside floodplain forest ● Alburgh Dunes State Park at North Hero is noted for its size, relatively ● Lake Champlain Bikeways undisturbed condition and the valuable wildlife habitat it provides. For More Information contact: Wildlife habitat improvements at North Hero North Hero State Park State Park have yielded tangible results. White- 3803 Lakeview Drive tailed deer are common, as are a variety of North Hero, VT 05474 migratory waterfowl - mallards, black and wood (802) 372-8727 (Operating Season) ducks nest in the wooded wetlands. Ruffed Or Call grouse and American woodcock find suitable VT State Parks Reservations Center breeding and nesting habitat here as well.
    [Show full text]
  • Brief Introduction Camp Plymouth State Park
    State Parks In Vermont: Brief Introduction by newsdesk Camp Plymouth State Park :The site of Camp Plymouth was at one time thought to have been used as an encampment by soldiers of the Revolutionary War in 1777. The Boy Scouts used this area until 1984 when it became a state park. Camp Plymouth State Park is located in the town of Plymouth on the east shore of Echo Lake. The total acreage is 295 acres of which 46 acres comprise the developed portion of the park. The balance (249 acres) contains hiking trails, fishing, hunting, gold panning, and primitive camping, but is largely forestry oriented. Fort Dummer State Park :The park was named after Fort Dummer, the first permanent white settlement in Vermont. Built on the frontier in 1724, it was initially the gateway to the early settlements along the banks of the Connecticut River. Forty-three English soldiers and twelve Mohawk Indians manned the fort in 1724 and 1725. Later, the fort protected what was then a Massachusetts colony from an invasion by the French and Indians. Made of sturdy white pine timber, stacked like a log cabin, Fort Dummer served its purpose well. The park overlooks the site of Fort Dummer which was flooded when the Vernon Dam was built on the Connecticut River in 1908. This site can be seen from the northernmost scenic vista on the Sunrise Trail. It is now underwater near the lumber company located on the western bank of the river. Knight Point State Park :Knight Point on North Hero Island opened as a state park in 1978.
    [Show full text]
  • Dune Nourishment Fact Sheet
    StormSmart Coasts StormSmart Properties Fact Sheet 1: Artificial Dunes and Dune Nourishment The coast is a very dynamic environment and coastal shorelines—especially beaches, dunes, and banks—change constantly in response to wind, waves, tides, and other factors such as seasonal variation, sea level rise, and human alterations to the shoreline system. Consequently, many coastal properties are at risk from storm damage, erosion, and flooding. Inappropriate shoreline stabilization methods can actually do more harm than good by exacerbating beach erosion, damaging neighboring properties, impacting marine habitats, and diminishing the capacity of beaches, dunes, and other natural landforms to protect inland areas from storm damage and flooding. StormSmart Properties—part of the Massachusetts Office of Coastal Zone Management’s (CZM) StormSmart Coasts program—provides coastal property owners with important information on a range of shoreline stabilization techniques that can effectively reduce erosion and storm damage while minimizing impacts to shoreline systems. This information is intended to help property owners work with consultants and other design professionals to select the best option for their circumstances. What Are Artificial Dunes and Dune Nourishment? A dune is a hill, mound, or ridge of sediment that No shoreline stabilization option permanently stops has been deposited by wind or waves landward of all erosion or storm damage. The level of protection a coastal beach. In Massachusetts, the sediments provided depends on the option chosen, project design, that form beaches and dunes range from sand to and site-specific conditions such as the exposure to gravel- and cobble-sized material. An artificial dune storms. All options require maintenance, and many is a shoreline protection option where a new mound also require steps to address adverse impacts to of compatible sediment (i.e., sediment of similar the shoreline system, called mitigation.
    [Show full text]