Forestry Habitat Management Guidelines for Vernal Pool Wildlife
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Wetland Restoration USING the Ground Water TECHNIQUE
Wetland ResTORATION USING THE Ground water TECHNIQUE How to build a ground water wetland three important vernal pool zones A ground water wetland fills with water the way a hand-dug well does, by exposing a high water table near the surface. Check for a high water table near a woodland oasis The vernal pool basin or depression is the area that floods in the fall or the center of a potential restoration site. Dig a hole at least 3 feet deep with a spring. This is where vernal pool amphibians and invertebrates breed and post-hole digger, soil auger, or shovel. Watch for water seeping into the hole A vernal pool is like a small oasis of food, water, and shelter for all kinds of lay their eggs, and their young hatch out, feed, and develop (Brown and from the bottom and sides. A high water table will fill the hole partially or woodland wildlife. Large game species such as turkeys, deer, and bears frequent Jung, 2005). The vernal pool basin is the core wetland area protected by state completely with water; listen for the slurp of water as a soil auger is removed. vernal pools, along with a variety of other wildlife including bats, ducks, and federal regulations. The vernal pool basin should be designated as a ‘no Clay soils are not needed to build a ground water wetland because the songbirds, turtles, and snakes. Vernal pools are unique among wetlands disturbance zone.’ depression simply exposes the water table. A seasonally high water table can because they support specialized pool-breeding salamanders, frogs, insects, The vernal pool envelope is the upland habitat immediately surrounding be hard to detect during the summer or any period of drought (Biebighauser, and crustaceans. -
Leaf Litter Decomposition in Vernal Pools of a Central Ontario Mixedwood Forest
Leaf Litter Decomposition in Vernal Pools of a Central Ontario Mixedwood Forest by Kirsten Verity Otis A Thesis presented to The University of Guelph In partial fulfilment of requirements for the degree of Master of Science in Environmental Science Guelph, Ontario, Canada © Kirsten V. Otis, July, 2012 ABSTRACT LEAF LITTER DECOMPOSITION IN VERNAL POOLS OF A CENTRAL ONTARIO MIXEDWOOD FOREST Kirsten V. Otis Advisors: University of Guelph, 2012 Dr. Jonathan Schmidt Dr. Shelley Hunt Vernal pools are small, seasonally filling wetlands found throughout forests of north eastern North America. Vernal pools have been proposed as potential 'hot spots' of carbon cycling. A key component of the carbon cycle within vernal pools is the decomposition of leaf litter. I tested the hypothesis that leaf litter decomposition is more rapid within vernal pools than the adjacent upland. Leaf litter mass losses from litterbags incubated in situ within vernal pools and adjacent upland habitat were measured periodically over one year and then again after two years. The experiment was carried out at 24 separate vernal pools, over two replicate years. This is a novel degree of replication in studies of decomposition in temporary wetlands. Factors influencing decomposition, such as duration of flooding, water depth, pH, temperature, and dissolved oxygen were measured. Mass loss was greater within pools than adjacent upland after 6 months, equal after 12 months, and lower within pools than adjacent upland after 24 months. This evidence suggests that vernal pools of Central Ontario are 'hot spots' of decomposition up to 6 months, but not after 12 and 24 months. In the long term, vernal pools may reduce decomposition rates, compared to adjacent uplands. -
Biological Resources Assessment the Ranch ±530- Acre Study Area City of Rancho Cordova, California
Biological Resources Assessment The Ranch ±530- Acre Study Area City of Rancho Cordova, California Prepared for: K. Hovnanian Homes October 13, 2017 Prepared by: © 2017 TABLE OF CONTENTS 1.0 Introduction ......................................................................................................................... 1 1.1. Project Description ........................................................................................................... 1 2.0 Regulatory Framework ........................................................................................................ 2 2.1. Federal Regulations .......................................................................................................... 2 2.1.1. Federal Endangered Species Act ............................................................................... 2 2.1.2. Migratory Bird Treaty Act ......................................................................................... 2 2.1.3. The Bald and Golden Eagle Protection Act ............................................................... 2 2.2. State Jurisdiction .............................................................................................................. 3 2.2.1. California Endangered Species Act ........................................................................... 3 2.2.2. California Department of Fish and Game Codes ...................................................... 3 2.2.3. Native Plant Protection Act ..................................................................................... -
Portsmouth Vernal Pool Inventory
Portsmouth Vernal Pool Inventory Prepared for: City of Portsmouth, NH Conservation Commission Prepared by: 122 Mast Road, Suite 6, Lee, NH 03861 in cooperation with The City of Portsmouth Planning Department and October 2008 TABLE OF CONTENTS I. Executive Summary II. Vernal Pools Defined III. Methodology IV. Vernal Pool Documentation Sheet V. Findings and Focus Area Summaries VI. Focus Area and Pool Location Maps VII. References Appendices A. Vernal Pool Documentation Sheets B. Proposed Revisions to Wetland Protection Regulations C. Aerial Photo Field Sheets City of Portsmouth Vernal Pool Inventory Report Page 1 I. EXECUTIVE SUMMARY West Environmental, Inc. (WEI) conducted a city-wide Vernal Pool Inventory to locate, document and map vernal pools in Portsmouth. This effort was coordinated with the Portsmouth Planning Department and Conservation Commission to help the City of Portsmouth in vernal pool identification and mapping. The goal of this project was to locate isolated wetlands that provide vernal pool habitat. Currently the City of Portsmouth’s wetland regulations exempt wetlands less than 5,000 square feet from the local 100’ buffer zone. This study identified smaller wetlands which have the potential to provide vernal pool habitat that may deserve the 100 foot buffer protection. It should be noted that vernal pool habitat can exist in a variety of freshwater wetlands including larger red maple swamps. These areas were also mapped when encountered. A field workshop was held for the Conservation Commission members to give them hands-on training in vernal pool ecology. The results of this Vernal Pool Inventory were presented to the Portsmouth Conservation Commission in July of 2008. -
Vernal Pool Vernal Pool, Page 1 Michael A
Vernal Pool Vernal Pool, Page 1 Michael A. Kost Michael Overview: Vernal pools are small, isolated Introduction and Definitions: Temporary water wetlands that occur in forested settings throughout pools can occur throughout the world wherever the Michigan. Vernal pools experience cyclic periods ground or ice surface is concave and liquid water of water inundation and drying, typically filling gains temporarily exceed losses. The term “vernal with water in the spring or fall and drying during pool” has been widely applied to temporary pools the summer or in drought years. Substrates that normally reach maximum water levels in often consist of mineral soils underlain by an spring (Keeley and Zedler 1998, Colburn 2004). impermeable layer such as clay, and may be In northeastern North America, vernal pool and covered by a layer of interwoven fibrous roots similar interchangeable terms have focused even and dead leaves. Though relatively small, and more narrowly upon pools that are relatively small, sometimes overlooked, vernal pools provide critical are regularly but temporarily flooded, and are habitat for many plants and animals, including rare within wooded settings (Colburn 2004, Calhoun species and species with specialized adaptations for and deMaynadier 2008, Wisconsin DNR 2008, coping with temporary and variable hydroperiods. Ohio Vernal Pool Partnership 2009, Vermont Vernal pools are also referred to as vernal ponds, Fish & Wildlife Department 2004, Tesauro 2009, ephemeral ponds, ephemeral pools, temporary New York Natural Heritage Program 2009, pools, and seasonal wetlands. Commonwealth of Massachusetts Division of Michigan Natural Features Inventory P.O. Box 30444 - Lansing, MI 48909-7944 Phone: 517-373-1552 Vernal Pool, Page 2 Fisheries and Wildlife 2009, Maine Department of community types (see Kost et al. -
Species of Greatest Conservation Need Species Accounts
2 0 1 5 – 2 0 2 5 Species of Greatest Conservation Need Species Accounts Appendix 1.4C-Amphibians Amphibian Species of Greatest Conservation Need Maps: Physiographic Provinces and HUC Watersheds Species Accounts (Click species name below or bookmark to navigate to species account) AMPHIBIANS Eastern Hellbender Northern Ravine Salamander Mountain Chorus Frog Mudpuppy Eastern Mud Salamander Upland Chorus Frog Jefferson Salamander Eastern Spadefoot New Jersey Chorus Frog Blue-spotted Salamander Fowler’s Toad Western Chorus Frog Marbled Salamander Northern Cricket Frog Northern Leopard Frog Green Salamander Cope’s Gray Treefrog Southern Leopard Frog The following Physiographic Province and HUC Watershed maps are presented here for reference with conservation actions identified in the species accounts. Species account authors identified appropriate Physiographic Provinces or HUC Watershed (Level 4, 6, 8, 10, or statewide) for specific conservation actions to address identified threats. HUC watersheds used in this document were developed from the Watershed Boundary Dataset, a joint project of the U.S. Dept. of Agriculture-Natural Resources Conservation Service, the U.S. Geological Survey, and the Environmental Protection Agency. Physiographic Provinces Central Lowlands Appalachian Plateaus New England Ridge and Valley Piedmont Atlantic Coastal Plain Appalachian Plateaus Central Lowlands Piedmont Atlantic Coastal Plain New England Ridge and Valley 675| Appendix 1.4 Amphibians Lake Erie Pennsylvania HUC4 and HUC6 Watersheds Eastern Lake Erie -
Blue-Spotted Salamander
Species Status Assessment Class: Amphibia Family: Ambystomatidae Scientific Name: Ambystoma laterale Common Name: Blue-spotted salamander Species synopsis: The blue-spotted salamander has the northernmost distribution of any Ambystoma species, occurring in east-central North America as far north as Labrador, with its distribution dipping southward into the northeastern United States only as far as northern New Jersey. In New York, this salamander occurs in a patchy distribution outside of high elevation areas; its occurrence on Long Island is only in the farthest eastern reaches. Blue-spotted salamander habitat is the moist forest floor of deciduous or mixed woodlands near ephemeral bodies of water. Reliable population trends are not available for this salamander. Hybridization occurs between blue-spotted salamander and Jefferson salamander (A. jeffersonianum). Broadly referred to as the Jefferson complex, the variety of hybrids includes up to five different chromosomal combinations. Some of the hybrids have been called Tremblay’s salamander or silvery salamander, but most references are to “Jefferson complex.” This unusual situation has lead to difficulty in defining the distribution of blue-spotted salamander and Jefferson salamander, the hybrids of which are very difficult to distinguish, typically, without genetic testing in conjunction with their appearance. In Connecticut, the blue-spotted diploid and the blue-spotted complex have been listed individually, as Threatened and Special Concern respectively but no other state or province has made this distinction in listing status. 1 I. Status a. Current and Legal Protected Status i. Federal ___Not Listed_______________________ Candidate? ___No____ ii. New York ___Special Concern; SGCN_____________________________________ b. Natural Heritage Program Rank i. Global _____G5__________________________________________________________ ii. -
Pennsylvania Statewide Seasonal Pool Ecosystem Classification
Pennsylvania Statewide Seasonal Pool Ecosystem Classification Description, mapping, and classification of seasonal pools, their associated plant and animal communities, and the surrounding landscape April 2009 Pennsylvania Natural Heritage Program i Cover photo by: Betsy Leppo, Pennsylvania Natural Heritage Program ii Pennsylvania Natural Heritage Program is a partnership of: Western Pennsylvania Conservancy, Pennsylvania Department of Conservation and Natural Resources, Pennsylvania Fish and Boat Commission, and Pennsylvania Game Commission. The project was funded by: Pennsylvania Department of Conservation and Natural Resources, Wild Resource Conservation Program Grant no. WRCP-06187 U.S. EPA State Wetland Protection Development Grant no. CD-973493-01 Suggested report citation: Leppo, B., Zimmerman, E., Ray, S., Podniesinski, G., and Furedi, M. 2009. Pennsylvania Statewide Seasonal Pool Ecosystem Classification: Description, mapping, and classification of seasonal pools, their associated plant and animal communities, and the surrounding landscape. Pennsylvania Natural Heritage Program, Western Pennsylvania Conservancy, Pittsburgh, PA. iii ACKNOWLEDGEMENTS We would like to thank the following organizations, agencies, and people for their time and support of this project: The U.S. Environmental Protection Agency (EPA) and the Pennsylvania Department of Conservation and Natural Resources (DCNR) Wild Resource Conservation Program (WRCP), who funded this study as part of their effort to encourage protection of wetland resources. Our appreciation to Greg Czarnecki (DCNR-WRCP) and Greg Podniesinski (DCNR-Office of Conservation Science (OCS)), who administered the EPA and WRCP funds for this work. We greatly appreciate the long hours in the field and lab logged by Western Pennsylvania Conservancy (WPC) staff including Kathy Derge Gipe, Ryan Miller, and Amy Myers. To Tim Maret, and Larry Klotz of Shippensburg University, Aura Stauffer of the PA Bureau of Forestry, and Eric Lindquist of Messiah College, we appreciate the advice you provided as we developed this project. -
Annual Migrations of Forest Amphibians
Annual Migrations of Forest Amphibians Photo by L. Heady Laura Heady Conservation and Land Use Coordinator Hudson River Estuary Program Hudson River Estuary …an arm of the sea • 153 miles from NY Harbor to Troy • Tidal to Troy Dam • ~60 tributaries to Hudson Photo by L. Heady • 85% of NY’s amphibians (28 species) are found in the watershed! (Penhollow et al. 2006) Photo by Laura Heady Photo by NYSDEC Today’s Focus: Vernal Pool Breeding Amphibians Photo by Erik Kiviat Photo by Charlie West Exciting Facts about Pool-Breeding Amphibians in the Hudson Valley • They are terrestrial and live in the forest! • They breed in vernal pools! • Their larvae are aquatic! Photos by L. Heady A B Forest Habitat Vernal Pool Habitat • fallen logs • surrounded by forest • leaf litter • isolated wetland • small animal burrows • seasonal inundation Photos by L. Heady salamander larvae wood frog tadpoles salamander egg masses Heady L. Photos by m spotted salamander a Photo by Laura Heady n y Photo by L. Heady Jefferson’s salamander blue-spotted salamander Photo by Laura Heady Photo by Erik Kiviat These commonly hybridize. Jefferson/blue-spotted s salamander complex o m e Photo by Josh Hunn Jefferson/blue-spotted salamander complex Photo by Brian Houser Jefferson/blue-spotted salamander complex Photo by Jim Clayton marbled salamander f e w (breeds in the fall) Photo by Brian Houser m wood frog a n y Photo by M. Barnhart wood frog More! Exciting Facts about Pool-Breeding Amphibians in the Hudson Valley • They are largely nocturnal. • They practice cutaneous air exchange! Photos by L. -
2.3 Avian Uses of Vernal Pools and Implications for Conservation Practice
Avian Uses of Vernal Pools and Implications for Conservation Practice JOSEPH G. SILVEIRA U. S. Fish and Wildlife Service, Sacramento National Wildlife Refuge Complex, Willows, CA 95988 ([email protected]) ABSTRACT. Vernal pool landscapes consist of vernal pools and their surrounding physiographical and biological environ- ments. They provide important habitats for both resident and migratory birds. Avian species are adapted to exploit the various zones and hydrologic phases of vernal pools which are characterized by spatial and temporal patterns of wet to dry habitats. Waterfowl and shorebirds use different types of wetland habitats in relation to their annual behavioral and energy cycle. During the spring, ducks feed on invertebrates which are abundant in ephemeral wetlands such as vernal pools. Invertebrates are important sources of protein and calcium needed for migration and reproduction. Cackling and Ross’ geese, during spring hyperphagia, spend long hours grazing on protein rich plants in herbaceous habitats adjacent to vernal pools. Several species of shorebirds are observed in vernal pool landscapes during winter, spring migration, and nesting periods. On a local scale, vernal pools are part of a complex of habitats where a diversity of birds use various resources. On a regional scale, vernal pool landscapes of the Central Valley’s eastern margin enhance migratory bird habitats of the valley floor. Vernal pools are also significant on a continental scale, providing vital links in the California portion of the Pacific Flyway corridor. Vast, intact vernal pool landscapes are necessary for continued large scale avian use. Conservation ease- ments that protect core areas, and land management agreements which include livestock grazing to maintain avian diversity, are needed to protect irreplaceable vernal pool landscapes in the future. -
Species Assessment for Jefferson Salamander
Species Status Assessment Class: Amphibia Family: Ambystomidae Scientific Name: Ambystoma jeffersonianum Common Name: Jefferson salamander Species synopsis: The distribution of the Jefferson salamander is restricted to the northeastern quarter of the United States extending as far to the southwest as Illinois and Kentucky; the species is represented in Canada only in a small area of southern Ontario. The habitat includes upland deciduous or mixed woodlands as well as bottomland forests adjacent to disturbed and agricultural lands. Breeding occurs in temporary ponds or semi-permanent wetlands (Gibbs et al. 2007). Hybridization occurs between the Jefferson salamander and the blue-spotted salamander (A. laterale). Broadly referred to as the Jefferson complex, the variety of hybrids includes up to five different chromosomal combinations. Some of the hybrids have been called Tremblay’s salamander or silvery salamander, but most references are to “Jefferson complex.” This unusual situation has lead to difficulty in defining the distribution of blue-spotted salamander and Jefferson salamander, the hybrids of which are very difficult to distinguish, typically, without genetic testing in conjunction with their appearance. I. Status a. Current and Legal Protected Status i. Federal ____ Not Listed_____________________ Candidate? __No_____ ii. New York ____Special Concern; SGCN___________________________________ b. Natural Heritage Program Rank i. Global ____G4____________________________________________________________ ii. New York ____S4_____________________ Tracked by NYNHP? ___No____ Other Rank: Species of Northeast Regional Conservation Concern (Therres 1999) Species of Severe Concern and High Responsibility (NEPARC 2010) 1 Status Discussion: Jefferson salamander is considered to be locally abundant in suitable habitat across New York. It has been designated as a Species of Regional Conservation in the Northeast due to its unknown population status and taxonomic uncertainty (Therres 1999). -
Terrestrial Influences on the Macroinvertebrate Biodiversity of Temporary Wetlands
TERRESTRIAL INFLUENCES ON THE MACROINVERTEBRATE BIODIVERSITY OF TEMPORARY WETLANDS Michael A. Plenzler A Dissertation Submitted to the Graduate College of Bowling Green State University in partial fulfillment of the requirements for the degree of DOCTOR OF PHILOSOPHY December 2012 Committee: Dr. Helen Michaels, Advisor Dr. Enrique Gomezdelcampo Graduate Faculty Representative Dr. Jeff Miner Dr. Karen Root Dr. Amy Downing ! ii! ABSTRACT Dr. Helen J. Michaels, Advisor Vernal pools are temporary wetlands and local-scale biodiversity hot spots for a variety of amphibians, macroinvertebrates, and plants because their seasonal drying prevents the establishment of predatory fish populations. Vernal pools are often of conservation concern because of the amphibian populations; however, the emphasis on these organisms often eclipses the macroinvertebrates, which are important predators, prey, and nutrient cyclers in wetlands and the surrounding habitat. Hydroperiod and water chemistry are thought to be the primary regulators of vernal pool macroinvertebrates, but the surrounding habitat also affects these organisms. Specifically, canopy cover and forest composition can alter the autochthonous and allochthonous carbon sources for wetland food webs. My research objectives were to understand how variations in these factors affect macroinvertebrate diversity and community composition. In 2009, I conducted a field survey of fifteen vernal pools that varied in area, depth, hydroperiod, canopy and surrounding land use. I measured several habitat conditions, assessed the biotic communities of these wetlands, and found that canopy cover influenced bottom-up productivity and macroinvertebrate diversity. I used the results of this study to determine how known macroinvertebrate communities respond to variation in canopy cover in mesocosm wetlands. The low canopy treatments sustained the highest macroinvertebrate abundance, family richness, and Shannon diversity, as greater algal productivity increased resources available to support the macroinvertebrate communities.