Oak Savanna Restoration

Project Schedule Restoring Oak Savanna 2020: Initial removal of trees and shrubs Oak savannas exist at the border of two of Minnesota’s major biomes – prairie Today, most of Minnesota’s historical oak savanna has been lost due to 2021: Site preparation (fire, and deciduous forests. Neither fully forest nor fully grassland, these habitats intensive or suppressed grazing, fire suppression, and introduction of other herbicide, plowing/disking) nurture many of the same flowers and grasses that grow in the prairie but also plant species. Currently, Washington County is restoring 231 acres of prairie 2021: Seeding feature sprawling bur oaks that create a partial forest canopy. and oak savanna here in Lake Elmo Park Reserve by restoring species to the 2022: Establishment mowing landscape to improve wildlife and pollinator habitat. To restore Oak savanna, Historically, oak savanna habitat existed in locations where the Dakota Native and haying common buckthorn, honeysuckle, amur maple and box elder are being removed American people lived. The Dakota people intentionally set fires to improve the 2022-2023: Spot treatment of to encourage future oak regeneration and a dense groundcover. Funding for habitat for both wild game and foraging around. This disturbance attracted herds noxious weeds this project was provided from the Outdoor Heritage Fund as appropriated of bison which grazed on the new prairie grasses. In areas where fire and grazing by the Minnesota State Legislature and recommended by the Lessard-Sams Future: Use of conservation based merge, Bur Oaks established due to their thick bark and ability to withstand fire. Outdoor Heritage Council (LSOHC) to restore, protect, and enhance Minnesota’s grazing and haying and controlled Oak savanna is home to a variety of wildlife including deer, turkeys, redheaded burns wetlands, prairies, forests, and habitat for fish, game, and wildlife. woodpeckers, and the federally endangered Rusty Patched bumblebee. *For more information, contact the park office at 651-430-8370 The red-headed woodpecker is an oak-savanna specialist, nesting in cavities of mature oak trees and caching acorns for food. Habitat loss across the state accounts for nearly an 80 percent decline in population since 2004, according to a 2014 Audubon Minnesota report. Degraded condition Thinning & buckthorn removal Restored oak savanna Oak Savanna Ecosystem The oak savanna ecosystem is largely dependent on landscape disturbances such as fire and grazing. Fire was intentionally set to clear shrubs and dead vegetation, which would attract wild game and improve foraging areas. Bison were also attracted to these areas and would prevent woody trees and shrubs from establishing. Prescribed burn Prescribed grazing Seeding Conservation grazing.

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Appendix L: Oak Savanna Definition
Appendix L: Oak Savanna Definition Appendix L: Oak Savanna Definition Working Definition of “Savanna” for shaded environments under trees, shifting as the tree canopy becomes more open or closed. Herba- Restoration Efforts at Crane Meadows ceous species typical of prairie and forest co-occur; NWR in addition to a set of very specific savanna species (see lists below) that have high fidelity to this com- General Definition of Southern Dry Savanna: munity type (Texler Personal commun., Drobney Personal commun. (Buchanan 1996). This spatial Savanna habitat at Crane Meadows NWR, like variation within the understory is a function of the savanna across its range, is a fire-dependent, varying degrees of species tolerance to shade and dynamic community characterized by scattered sun. Forbs are an essential component of the under trees or groves of trees, mostly comprised of oaks - story. Another important component of savanna (Quercus sp.) with a canopy cover ranging from 10– 70%, but more typically between 25-50%; and a understory is the shrub layer. The understory of basal area (BA) of 5-50 sq ft / acre. A wide range is savanna on the Anoka Sandplain, including those at Crane Meadows NWR, can be present with or with- used because canopy cover is not the most impor- tant characteristic that defines savanna and also out shrubs. The extent of shrub density is depen- because savanna ecosystems are dynamic and are dent on the subtype savanna classification and the frequency of fire (Law et al. 1994, Swanson 2008, associated with a natural range of variation through space and time.
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Black Oak Savanna Nature Centres 5 Summer Camp Sign-Up 6 by Kevin Tupman Oak Savanna
THE GRAND STRATEGY NEWSLETTER Volume 15, Number 3 - May-June 2010 Grand River The Grand: Conservation A Canadian Authority Heritage River Feature Fire restores a rare savanna forest 1 Milestones Byng island’s 50th 2 Look Who’s Taking Action Caring for bluebirds 3 Swallow habitat 4 Rotary forest 5 Fire restores a rare forest: What’s happening New programs at black oak savanna nature centres 5 Summer camp sign-up 6 By Kevin Tupman oak savanna. Older oaks now existing within the SWP update 6 Natural Heritage Specialist area are a testament to the vision, progressive for Grand River a grand its time, expressed in the master plan. place to paddle 7 ost people know that some plants and ani- Fire is necessary because this rare ecosystem Water festival photo 7 Mmals are at risk, such as the bald eagle and is sustained by fire. Historically, fire resulted American ginseng, but not many people realize from either lightning or aboriginal inhabitants. Now Available that communities such as forests, can also be at Fire ensures that savanna areas do not turn into Grand new risk. dense forests. Only trees with a high tolerance fishing book 7 It is true that sugar maple woodlots and pine for fire, such as the black oak, are able to sur- plantations are commonplace. However, the vive. European settlers cleared much of the savanna Calendar 8 GRCA is restoring one of the rarest of forests — for agriculture. They also suppressed the fires. a black oak savanna close to Apps’ Mill in Brant This meant that surviving pockets of savanna Cover photo County.
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Robert Grau Memorial Oak Savanna Trail Guide
Robert Grau Robert Grau was a forester and a true conservationist. He was a charter member of Robert Grau the Clayton County Conservation Board from 1958-1978, and he was one of the first to Memorial Oak reconstruct a prairie in Clayton County in the late 1970's . The reconstruction of Savanna Trail this Oak Savanna is dedicated to his memory. Guide 29862 Osborne Road Elkader, IA 52043 Clayton County (563)-245-1516 Robert Grau with his son and grandsons Conservation Board Welcome! Prairie Reconstruction Oak Savanna Welcome to the Robert Grau Memorial Oak As you make your way up the first hill, you’ll notice a At the top of the hill, you have a good view of the oak Savanna and Trail! Use this brochure to help large open prairie off to the right. Prairie was once savanna. Savannas are open landscapes of widely guide you along the trail. We hope you enjoy common in NE Iowa. The original spaced, broad-crowned trees and a diverse mix of your visit! prairie around the village of Motor shrubs, grasses, and wildflowers. Once common in was turned into farmland when the NE Iowa’s hills and river valleys, savannas are now Limestone Kiln Klink family bought Motor Mill and rare, due to land use change for farming and building. At the beginning of the trail next to the road, just past surrounding buildings in 1903. the Cooperage, is where a lime kiln was once located. Clayton County Conservation Limestone Quarry acquired the site in 1983 and has The kiln would have been used during the late 1860’s Once at the top of the hill, you will notice a large since restored this area to prairie when Motor Mill was being constructed.
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Community Abstract Oak Openings
Oak Openings CommunityOak Openings,Abstract Page 1 Historical Range Prevalent or likely prevalent Infrequent or likely infrequent Photo by Michael A. Kost Absent or likely absent Overview: Oak openings is a fire-dependent, savanna climatic tension zone. In the 1800s, oak openings were type dominated by oaks, having between 10 and located in the south-central Lower Peninsula of Michigan 60% canopy, with or without a shrub layer. The on sandy glacial outwash and coarse-textured moraines predominantly graminoid ground layer is composed (Wing 1937, Comer et al. 1995, NatureServe 2004). Oak of species associated with both prairie and forest openings occurred within the range of bur oak plains communities. Oak openings are found on dry-mesic and oak barrens, with oak openings dominating more on loams and occur typically on level to rolling topography dry-mesic to mesic soils, bur oak plains occupying more of outwash and coarse-textured end moraines. Oak mesic, flat sites in the southwestern part of the Lower openings have been nearly extirpated from Michigan; Peninsula, and oak barrens thriving on droughty sites. only two small examples have been documented. These similar oak savanna types often graded into each other. Oak openings were historically documented in Global and State Rank: G1/S1 the following counties: Allegan, Barry, Berrien, Branch, Calhoun, Cass, Clinton, Eaton, Genesee, Hillsdale, Range: Oak savanna1 and prairie communities reached Ingham, Ionia, Jackson, Kalamazoo, Kent, Lapeer, their maximum coverage in Michigan approximately Lenawee, Livingston, Macomb, Montcalm, Monroe, 4,000-6,000 years ago, when post-glacial climatic Newaygo, Oakland, Ottawa, Shiawassee, St. Joseph, Van conditions were comparatively warm and dry.
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Functional Phenology of a Texas Post Oak Savanna from a CHRIS PROBA Time Series
remote sensing Article Functional Phenology of a Texas Post Oak Savanna from a CHRIS PROBA Time Series Michael J. Hill 1,2,* , Andrew Millington 2 , Rebecca Lemons 1 and Cherie New 1 1 Department of Earth System Science and Policy, University of North Dakota, Grand Forks, ND 58202, USA; [email protected] (R.L.); [email protected] (C.N.) 2 College of Science and Engineering, Flinders University, Sturt Road, Bedford Park, South Australia 5042, Australia; andrew.millington@flinders.edu.au * Correspondence: [email protected]; Tel.: +61-413161853 Received: 19 September 2019; Accepted: 13 October 2019; Published: 15 October 2019 Abstract: Remnant midwestern oak savannas in the USA have been altered by fire suppression and the encroachment of woody evergreen trees and shrubs. The Gus Engeling Wildlife Management Area (GEWMA) near Palestine, Texas represents a relatively intact southern example of thickening and evergreen encroachment in oak savannas. In this study, 18 images from the CHRIS/PROBA (Compact High-Resolution Imaging Spectrometer/Project for On-Board Autonomy) sensor were acquired between June 2009 and October 2010 and used to explore variation in canopy dynamics among deciduous and evergreen trees and shrubs, and savanna grassland in seasonal leaf-on and leaf-off conditions. Nadir CHRIS images from the 11 useable dates were processed to surface reflectance and a selection of vegetation indices (VIs) sensitive to pigments, photosynthetic efficiency, and canopy water content were calculated. An analysis of temporal VI phenology was undertaken using a fishnet polygon at 90 m resolution incorporating tree densities from a classified aerial photo and soil type polygons.
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Bur Oak Savanna
Bur Oak Savanna 1992 Bur oak savanna remnants exist in the southern half of WNT. Native herbaceous vegetation typical of savanna exists in the understory and will serve as a fuel base for future prescribed burns. 1993 Much interest has been generated in savannas as a topic. In February 1993, the first North American Oak Savanna Conference was held in Chicago, Illinois. Refuge Biologist Drobney was a participant in an effort to share information and to draft a Midwest Savanna Ecosystem Recovery Plan. During the same conference, interest was generated in WNT’s savannas that have mesic to wet-mesic characteristics. Most of the current information about savannas has been derived from sand savannas. Sand savannas have been more likely to survive because they are less suited to agriculture and therefore less a subject to the plow. In addition, invasive woody species often tend to develop more slowly in dry sandy areas resulting in a longer time period prior to canopy closure. In some areas on WNT, prairie cord grass and other moisture loving species occur in the oak understory on hillsides associated with seeps. In other areas, savannas occur in relatively low moist areas. WNT, therefore, is potentially an important study site that could yield a better understanding of a once common kind of Midwestern oak savanna that is poorly understood and largely obliterated. 1998 In 1998, we cleared approximately 3 acres of trees in natural community remnants including Thorn Valley Savanna, Coneflower Prairie, Buzzard Head, and Don’s II. 1999 Hundreds of orchids of three species including twayblade (Liparis liliifolia), showy orchis (Galearis spectabilis), and nodding ladies’ tresses (Spiranthes cernua) were manifest and blooming profusely in summer of 1999 in the Buzzard Head Prairie remnant.
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East Central Plains (Post Oak Savanna)
TEXAS CONSERVATION ACTION PLAN East Central Texas Plains (Post Oak Savanna) ECOREGION HANDBOOK August 2012 Citing this document: Texas Parks and Wildlife Department. 2012. Texas Conservation Action Plan 2012 – 2016: East Central Texas Plains Handbook. Editor, Wendy Connally, Texas Conservation Action Plan Coordinator. Austin, Texas. Contents SUMMARY ..................................................................................................................................................... 1 HOW TO GET INVOLVED ............................................................................................................................... 2 OVERVIEW ..................................................................................................................................................... 3 RARE SPECIES and COMMUNITIES .............................................................................................................. 13 PRIORITY HABITATS ..................................................................................................................................... 13 ISSUES ......................................................................................................................................................... 19 CONSERVATION ACTIONS ........................................................................................................................... 28 ECOREGION HANDBOOK FIGURES Figure 1. ECPL Ecoregion with County Boundaries ......................................................................................
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Landowner's Guide to Restoring and Managing Oregon White Oak Habitats
ACKNOWLEDGEMENTS The landowner stories throughout the Guide would not have been possible without help from Lynda Boyer, Warren and Laurie Halsey, Mark Krautmann, Barry Schreiber, and Karen Thelen. The authors also wish to thank Florence Caplow and Chris Chappell of the Washington Natural Heritage Program and Anita Gorham of the Natural Resource Conservation Service (NRCS) for helping us be�er understand Oregon white oak plant community associations. John Christy of the Oregon Natural Heritage program provided data for mapping pre-se�lement vegetation of the Willame�e Valley. Karen Bahus provided invaluable technical editing and layout services during the preparation of the Guide. Finally, we offer our appreciation to the following members of the Landowner’s Guide Steering Commi�ee: Hugh Snook, Bureau of Land Management (BLM) - Commi�ee Leader, Bob Altman The American Bird Conservancy (ABC), Eric Devlin, The Nature Conservancy (TNC), Connie Harrington, U.S.D.A. Forest Service (USFS), Jane Kertis (USFS), Brad Kno�s, Oregon Department of Forestry (ODF), Rachel Maggi, Natural Resource & Conservation Service (NRCS), Brad Withrow-Robinson, Oregon State University Extension Service (OSU), and Nancy Wogen, BLM. These Commi�ee members reviewed earlier dra�s of our work and offered comments that led to significant improvements to the final publication. All photos were taken by the authors unless otherwise indicated. Landowner’s Guide to Restoring and Managing Oregon White Oak Habitats Less than 1% of oak-dominated habitats are protected in parks or reserves. Private landowners hold the key to maintaining this important natural legacy. Landowner’s Guide to Restoring and Managing Oregon White Oak Habitats GLOSSARY OF TERMS GLOSSARY OF TERMS Throughout this Landowner’s Guide, we have highlighted many terms in bold type to indicate that the term is defined in the glossary below.
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An Ecological Investigation Into a Remnant Oak·Savana in Southern Minnesota
AN ECOLOGICAL INVESTIGATION INTO A REMNANT OAK·SAVANA IN SOUTHERN MINNESOTA by Scott C. Laursen Submitted for Independent Research St. Olaf College Northfield, Minnesota May 1997 Abstract: A small forested plot in Northfield, MN was examined to determine if it is a remnant oak savanna and to gather baseline data to assess the area's present successional status. The canopy of the 90m X 90m test site was dominated by old growth Quercus macrocarpa (bur oaks). The plot was divided into periphery and interior according to the size of surrounding shade-tolerant saplings, and radiation levels in both areas were measured over three days. The height of each oak's lowest living lateral branch was recorded along with the number of dead branches below it. Spatial dispersion, coverage, and the map location of each old growth oak were also determined. A soil pit was dug in the remnant and a nearby late-successional forest plot. Nitrates, percent organic matter, and pH were compared between the remnant and the comparison plot. There were significant differences in radiation levels, lowest living lateral branches, and number of dead limbs below the lowest living branch between interior and periphery oaks. Results suggest that each shade-intolerant Quercus macrocarpa is being overtaken from its base up, as growing invasive species reduce its light. Dispersion tests revealed a slight tendency toward a contagious pattern in the oaks, especially in the southern corner of the plot. The oak coverage estimate was less than 70°/o and, therefore, within the classification range of an oak savanna ecosystem as defined by the state of Minnesota.
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A Potential Understory Flora for Oak Savanna in Iowa
Journal of the Iowa Academy of Science: JIAS Volume 103 Number 1-2 Article 4 1996 A Potential Understory Flora for Oak Savanna in Iowa Karl T. Delong Grinnell College Craig Hooper Grinnell College Let us know how access to this document benefits ouy Copyright © Copyright 1996 by the Iowa Academy of Science, Inc. Follow this and additional works at: https://scholarworks.uni.edu/jias Part of the Anthropology Commons, Life Sciences Commons, Physical Sciences and Mathematics Commons, and the Science and Mathematics Education Commons Recommended Citation Delong, Karl T. and Hooper, Craig (1996) "A Potential Understory Flora for Oak Savanna in Iowa," Journal of the Iowa Academy of Science: JIAS, 103(1-2), 9-28. Available at: https://scholarworks.uni.edu/jias/vol103/iss1/4 This Research is brought to you for free and open access by the Iowa Academy of Science at UNI ScholarWorks. It has been accepted for inclusion in Journal of the Iowa Academy of Science: JIAS by an authorized editor of UNI ScholarWorks. For more information, please contact [email protected]. ]our. Iowa Acad. Sci. 103(1-2):9-28, 1996 A Potential U nderstory Flora for Oak Savanna in Iowa KARL T. DELONG and CRAIG HOOPER Department of Biology and Conard Environmental Research Area Grinnell College, Grinnell, Iowa 50112 Oak savanna occurred in Iowa until the time of settlement and then was degraded rapidly. There were no scientific studies of savan na pnor to, or after, settlement, and now no high-quality examples exist within the state. To identify those vascular plants adapted to live m the u.nderstory of savai:ina we exammed reg10nal and local flora for species that occurred in both prairie and broken woodland, and for species that occurred m both openmgs and forest.
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Oak Opening (Global Rank G1; State Rank S1)
Oak Opening (Global Rank G1; State Rank S1) Overview: Distribution, Abundance, or control unwanted woody growth and invasive herbs and Environmental Setting, Ecological Processes encourage suppressed native groundlayer plants. In some res- Historically, Oak Openings occurred on dry to wet-mesic toration efforts, it has been deemed necessary to reintroduce sites across much of southern and western Wisconsin. Patch native plant species that have been lost. size and configuration varied greatly, and the community As defined by Curtis (1959), Oak Openings are oak-dom- was found as isolated groves, in draws between ridges, on inated savanna communities in which there was at least one tongue-like peninsulas, on steep slopes partially protected tree per acre but where total tree cover was less than 50%. by waterbodies or wetlands, and sometimes as extensive However, he also noted that the “density (of trees) per acre ecotonal areas separating open prairie from closed forest. was the most variable of all characteristics,” a key point for According to the interpretations of Curtis (1959) and Fin- managers and restoration planners. It’s also worth noting that ley (1976), Oak Openings covered approximately 5.5 million Oak Openings could grade seamlessly into communities still acres in southern Wisconsin at the time of the federal public influenced by and ultimately dependent on periodic wild- land survey in the mid-19th century. Only the vast (and vari- fire but characterized by increasing levels of canopy closure. able) Northern Mesic Forests in the northern part of the state A continuum of the fire-dependent “oak ecosystem” could were more extensive.
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Northern Oak Savanna
Rapid Assessment Reference Condition Model The Rapid Assessment is a component of the LANDFIRE project. Reference condition models for the Rapid Assessment were created through a series of expert workshops and a peer-review process in 2004 and 2005. For more information, please visit www.landfire.gov. Please direct questions to [email protected]. Potential Natural Vegetation Group (PNVG) R6NOKS Northern Oak Savanna General Information Contributors (additional contributors may be listed under "Model Evolution and Comments") Modelers Reviewers James Merzenich [email protected] David Cleland [email protected] Donald Dickman [email protected] Vegetation Type General Model Sources Rapid AssessmentModel Zones Woodland Literature California Pacific Northwest Local Data Great Basin South Central Dominant Species* Expert Estimate Great Lakes Southeast Northeast S. Appalachians QUAL CORY LANDFIRE Mapping Zones SCHIZ Northern Plains Southwest QUMA 41 51 SONU N-Cent.Rockies QUVE 49 52 ANGE 50 Geographic Range Northern oak savanna occurs in a complex, shifting mosaic with oak woodlands, barrens and prairies in the upper Midwest. This type occurs in southern Lower Michigan, northwestern Ohio, northern Indiana, northeastern Illinois, southern Wisconsin, and southeastern to northwestern Minnesota. This savanna/woodland/prairie type historically occurred as an ecotone between mesic hardwood forest and tallgrass prairie. Biophysical Site Description Northern oak savanna occurs primarily on level to rolling topography of glacial outwash plains, coarse- textured end moraines, and steep ice-contact features (Chapman 1984, Albert 1995, Cohen 2001, Michigan Natural Features Inventory 2003, Cohen 2004, NatureServe 2004). Soils are well-drained, moderately- fertile sands, loamy sands, sandy loams, and loams with medium-acid to neutral pH (5.6 to 7.3) and low water retaining capacity (Chapman 1984, Michigan Natural Features Inventory 2003, NatureServe 2004).
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