Invasive-Perennial Dominated Field to Conservation Meadow

Total Page:16

File Type:pdf, Size:1020Kb

Invasive-Perennial Dominated Field to Conservation Meadow Restoring Your Invasive Perennial-Dominated Grassland to Conservation Meadow The author of this Restoration Guide is Laura Phillips-Mao, University of Minnesota. Steve Chaplin, MN/ND/SD Chapter of The Nature Conservancy, administered the project and helped with production. Marybeth Block, Minnesota Department of Natural Resources, provided review and editorial comments. Susan Galatowitsch, University of Minnesota, contributed to an earlier version of this guide. ©The Nature Conservancy January 1, 2017 Funding for the development of this restoration guide was provided by the Minnesota Environment and Natural Resources Trust Fund as recommended by the Legislative-Citizen Commission on Minnesota Resources (LCCMR) through grant LCCMR092C. The Trust Fund is a permanent fund constitutionally established by the citizens of Minnesota to assist in the protection, conservation, preservation, and enhancement of the state’s air, water, land, fish, wildlife, and other natural resources. Currently 40% of net Minnesota State Lottery proceeds are dedicated to building the Trust Fund and ensuring future benefits for Minnesota’s environment and natural resources. Additional funding for the update and redesign of the guide was provided by a Working Lands Initiative grant from the Minnesota Department of Natural Resources. Cover photo taken at Twin Valley Prairie by Justin Meissen. interesting to people. Conservation meadow is Restoring Your Invasive not suitable for forage production, commercial Perennial-Dominated uses or high-impact recreational activities such as driving ATVs. Grassland to “Conservation Meadow” Compatible land uses include: In this guide, you will learn the basic steps to Carefully managed grazing for habitat restore a grassland dominated by invasive goals1 perennial weeds to a conservation meadow. Haying for habitat goals The precise restoration actions will depend on the particular features of your site as well as Occasional seed harvest your budget, preferences and project goals. Low-impact recreational activities, such as hiking, photography, or hunting When planning your restoration, we Conservation benefits include improved water recommend you consult with restoration quality, flood control, and habitat for birds, professionals to evaluate your site’s unique animals and insects. Conservation prairie can characteristics. Please visit also buffer high-quality native meadows and nature.org/MNPrairieRestorationGuides for prairies and support threatened and more information on who to contact or other endangered plants and animals that depend on publications that cover site assessment large contiguous areas of grassland. protocols. What is conservation Why restore invasive meadow? perennial-dominated grasslands? Conservation meadow is a wet grassland designed to closely mimic native wet prairie Restoring invasive perennial-dominated and sedge meadow using seed mixes that have grasslands to utility meadow increases the many native species adapted to the restoration diversity of species on the site and provides site. It occurs on poorly-drained, wet to valuable habitat for prairie wildlife and moderately wet soils that are saturated up to 8 pollinators. Invasive perennial-dominated weeks following snowmelt and are prone to grasslands have substantial coverage (>75%) of temporary ponding after large rainfall events. exotic invasive perennials, such as reed canary Conservation meadow often occurs in a grass, smooth brome and birdsfoot trefoil. transition zone between emergent marsh and Often used as pasture or hay fields, these sites upland prairie and may be either sedge- are dominated by aggressive species that dominated (“sedge meadow”) or grass- persist for many years and can quickly dominated (“wet prairie”) depending on the outcompete and suppress planted natives. duration of soil saturation. Reed canary grass is particularly common on wet sites and may require multiple years of repeated treatments to control. Invasive woody The diversity of plants in conservation meadow provides habitat and food for native wildlife and insects, including pollinators. A wide variety of flowering plants and grasses is also visually 1 Very wet sites are vulnerable to damage by trampling and are dominated by sedges, which are not preferred forage for cattle. Moderately wet sites, which are dominated by grasses and have a shorter duration of seasonal ponding, will generally be more suitable for grazing. 1 species may also be present and require What will it involve? additional removal strategies2. Invasive perennial-dominated grasslands are Meadow restoration typically includes these one of the most challenging starting conditions basic steps: for restoration, because they require substantial investment of time before and after seeding prairie species. Restoring these sites Site Assessment— Identify the site often requires multiple seasons of vegetation characteristics and define goals for the control prior to seeding, and attentive restoration. management through the seedling establishment phase and beyond. When Vegetation Removal – Remove existing possible, cropping these fields is an increasingly weeds and undesired vegetation from the popular and more affordable option for site to prevent aggressive weedy species achieving the level of weed control required for from out-competing native meadow plants. successful restoration. Additionally, if the site has been drained with drainage tiles or ditches, Seedbed Preparation – Prepare a seedbed to restoring hydrology by breaking tiles, plugging ensure good seed-soil contact and promote ditches, and—in some cases—installing water germination of planted seeds. control devices, will be required. Seeding/Planting – Select seed mixes and This guide assumes that your site is wet to seeding methods that are well suited to the moderately wet and has been drained via tiles site and project goals. Or, in the case of or ditches3. Sites that have not been drained small sites of less than half an acre, will not require the additional steps to restore consider hand-planting plugs for quicker the hydrology. results4. Hydrologic Restoration – Remove drainage features by breaking tile or plugging ditches to restore the site’s original soil moisture and seasonal flooding patterns. Establishment & Aftercare – Control weeds and promote the establishment and growth of meadow plants through the first few years after seeding. Long-term Management – Maintain the health and diversity of native meadow into the future. Restoring hydrology at Glacial Ridge © TNC\Jason Eckstein 2 If invasive trees and shrubs are present on site, refer to the restoration guide “Restoring your Woody-Invaded Meadow to Conservation Meadow” for information on controlling woody species. 3 For sites with moderate to dry soil moisture, refer to the restoration guide “Restoring your Invasive Perennial-Dominated Field to Conservation Prairie”. 4 Plugs are young plants sold in 4- or 6-packs. Plugs cost substantially more than seed, but they establish rapidly and can produce a resilient and visually appealing meadow more quickly than seeding, so it is often a preferred option for smaller sites. 2 How long will it take? What will it cost? On an invasive perennial-dominated grassland, The cost of the restoration will be influenced the initial site preparation typically requires at by: least one full calendar year prior to seeding. When possible, spending two growing seasons on thorough invasive species control prior to Management level required to control seeding will yield more optimal results. The weeds more you invest in weed control up front, the Species and number of species selected for less time and effort you will need to spend the seed mix controlling weeds in the long term. After the year it’s seeded, expect to spend at least three Cost of seed, which fluctuates from year to to five years on aftercare to ensure good year establishment of the conservation meadow. This period is referred to as the establishment Hydrologic factors, such as drainage type, phase of restoration. size and depth; soil type and sediment deposits; and whether management of wetland discharge is required After establishment, often after year five for Labor and equipment available for the conservation meadow, the long-term project management phase begins. Management actions are typically less frequent and intensive The cost estimate in this document will give than during the establishment phase, but are you a baseline for what you can expect to critical for maintaining the health and diversity spend through the initial establishment phase of the meadow into the future. of your restoration (i.e. through three years after seeding). It may be tempting to cut costs by reducing the number of species planted or the frequency of weed control activities. Be aware that these investments on the front end can actually save costs in the long run. A healthy and diverse meadow will be more resilient to disturbance, invasion by exotic species, and extreme weather events such as drought. Reed canary grass infested meadow near Bluestem Prairie ©TNC\Steve Chaplin 3 Invasive Perennial-Dominated Grassland to Conservation Meadow Restoration Guidelines Site assessment native vegetation. Restoration of wet prairie and sedge meadow communities almost always involves control and prevention of reed canary A successful meadow restoration is highly grass invasion. Thorough site preparation is dependent on specific characteristics of a site. critical prior to planting, because control
Recommended publications
  • Grassland Resources and Development of Grassland Agriculture in Temperate China
    124 Rangelands 10(3), June 1988 Grassland Resources and Development of Grassland Agriculture in Temperate China Zhu Tinachen Natural temperate grasslands occupy 2.4 million km2 or one-quarter ofthe area of China. They form a broad beltfrom the plains of the northeast to the Tibetan Plateau of the southwest (Fig. 1). The nature and distribution of thegrassland is determined in large part by the influence of the monsoon. In the north- east where the monsoon is well developed, the grassland owes its existenceto dry conditions in the spring. Westward and southwestward wherethe monsooninfluence is weaker, the grasslandsoccupy higherelevations (to as high as 5,000 m) in response to the semiarid and arid regional climate. Similarly, temperate grasslands occur at high elevations in mountains of the desert region in northwestern China, far beyond the continuous grassland belt. Some 4,000 species offlowering plants comprise thevegetation ofthese temper- ate grasslands.About 200 are important forage species. The livestock population in China is about 130 million Fig. I Steppe zone of China cattle units. Most of the livestock are dependent on these 1.Meadow steppe, 2.Typical steppe. 3.Desert steppe. 4. Shrub steppe. 5. Alpine steppe. natural temperategrasslands. GrasslandTypes responding to climate and distributed in the form of a belt. Meadows are not zonal; they are controlled by local envi- Based on the concept of zonal vegetation, the natural ronments.About 80 ofthe area of is occu- of China can be divided into two percent grassland temperategrasslands major pied by zone steppetypes and about 20 percent by meadow types: steppe and meadow.
    [Show full text]
  • Mid-Atlantic Native Meadows Guidelines for Planning, Preparation, Design, Installation, and Maintenance
    Mid-Atlantic Native Meadows Guidelines for Planning, Preparation, Design, Installation, and Maintenance Alice Sturm, Mahan Rykiel Associates Stephanie Frischie, Xerces Society for Invertebrate Conservation Mid-Atlantic Native Meadows Guidelines for Planning, Preparation, Design, Installation, and Maintenance Alice Sturm, Mahan Rykiel Associates Stephanie Frischie, Xerces Society for Invertebrate Conservation The Xerces Society is a nonprofit organization that protects the natural world by conserving invertebrates and their habitat. Established in 1971, the Society is a trusted source for science-based information and advice and plays a leading role in promoting the conservation of pollinators and many other invertebrates. We collaborate with people and institutions at all levels and our work to protect bees, butterflies, and other pollinators encompasses all landscapes. Our team draws together experts from the fields of habitat restoration, entomology, plant ecology, education, farming, and conservation biology with a single passion: Protecting the life that sustains us. The Xerces Society for Invertebrate Conservation 628 NE Broadway, Suite 200, Portland, OR 97232 Tel (855) 232-6639 Fax (503) 233-6794 www.xerces.org Regional offices from coast to coast The Xerces Society is an equal opportunity employer and provider. Xerces® is a trademark registered in the U.S. Patent and Trademark Office Founded in 1983, Mahan Rykiel Associates is a 35-person landscape architecture, urban design, and planning firm located in Baltimore, Maryland. The firm works across scales to imagine and realize projects that enrich the human condition and support vibrant natural systems. Research and discovery guide project development that includes public parks, civic plazas, state infrastructure, mixed-use housing, private residences, healthcare facilities, hotels, and commercial centers.
    [Show full text]
  • Wildflower Meadows
    Online edition: ISSN 2009-6852 National Biodiversity Data Series No. 13. Print edition: ISSN 2009-6844 How-to-guide Creation and management of a wildfl ower meadow All-Ireland Pollinator Plan e I m 2015-2020 r t p n l e e m C a e t n a t a D t i y o t i n s c r o e o iv rd d i io n B at l ed na by tio th Na e www.biodiversityireland.ie/pollinator-plan How-to-guide 4 “How can I create a What is a wildflower wildflower meadow for meadow? A wildfower meadow is many things to many pollinators?” people. To some, a wildfower meadow is a brightly This is the Pollinator Plan’s most frequently asked coloured feld made up of annual species such as question. If we want to ensure our pollinators poppies and cornfowers (left photo, below). These are there when we need them, providing enough were the “weeds” of cereals such as barley. With food (fowers) is key. Planting a native wildfower selective herbicides and improved seed cleaning meadow can help, but creating a sustainable, practices these species have declined. pollinator friendly meadow is more complex than most people realise. That is why the experts at Other people have in mind the traditional Irish EcoSeeds have collaborated with the Pollinator hay meadow (right photo, below). In the last 50 Plan to help produce this How-to-Guide. It will help years the practice of hay making has declined you plan for and carry out your wildfower project.
    [Show full text]
  • NEST OBSERVATIONS of the LONG-EARED OWL (Asio Otus) in BENTON COUNTY, OREGON, with NOTES on THEIR FOOD HABITS RICHARD T
    This file was created by scanning the printed publication. Errors identified by the software have been corrected; however, some errors may remain. NEST OBSERVATIONS OF THE LONG-EARED OWL (Asio otus) IN BENTON COUNTY, OREGON, WITH NOTES ON THEIR FOOD HABITS RICHARD T. REYNOLDS INTRODUCTION A nesting pair of long-eared owls was found 10 miles north of Corvallis, Benton County, Oregon, on 24 April, 1969. The pair was observed and photographed until 30 May, when the young left the nest. This is the third record of nesting Asio otus west of the Oregon Cascades. Gabrielson and Jewett (1940) reported that Pope collected eggs from a nest "presumablynear Sheridan" in 1894. Maser and Gordon (1965) found a nesting pair 21/2 miles north of Bellfountain, Benton County, on 13 May, 1964. HABITAT The owls were located in the north end of McDonald Forest at approx- imately 400 feet elevation. The nest was in a grove limited on the northern extreme by a small, unused grassy meadow which opened into a long shallow valley. The meadow, like the grove, had a gentle north slope and was interspersed with a few small white oaks (Quercus garryana). The grove itself was second-growth Douglas fir (Pseudotsuga menziesii), 10 to 12 inches D.B.H., with scattered white oaks and big-leaf maple (Acer macro- phyllum). The average height of the grove was approximately 40 feet. From the meadow's edge to the border of a small flat, 100 yards up the slope, the fir was dense. The canopy on the flat, 50 x 150 yards, was relatively open and more frequently interspersed with deciduous trees.
    [Show full text]
  • A Winter Roost of Long-Eared Owls
    A WINTER ROOST OF LONG-EARED OWLS by John W. Andrews, Lexington IntroduCtion During the winter of 1980-81 a remarkable roost of approx­ imately 21 Long-eared Owls CAsio otus) assembled at the DunbaCk Meadow Conservation Area (see referenCe 1) in Lexington. BeCause the Long-eared Owl is seldom seen by birders, the roost attracted considerable attention. During January and February approximately 400 persons visited the highly acCessible site to see these owls, and most were curious about the reasons for the unusual assem­ blage. Some returned several times, and three (myself together with Don and Lillian Stokes) undertook a study of the roost to learn as much as possible about the behav­ ior of the owls. We soon found that we were recording information that had never been reported in the ornithol­ ogiCal literature. The following summarizes our findings. BasiC faCts about the Long-eared Owl The Long-eared Owl is a medium-sized owl* which hunts open fields by night, often by coursing back and forth at low altitude. Its primary prey speCies is the Meadow Vole (Microtus pennsylvanicus), which Constitutes 75 to 95 per Cent of the winter diet (refs. 2 and 3). A Long-eared Owl must catch two or three of these meadow mice per night in order to survive. Wintering Long-eared Owls in Massachusetts roost almost exclusively in Coniferous woodlots. Communal winter roosts often occur in which individuals retire in Close proximity during the day and fan out at night to hunt nearby fields. Bent (ref. 4) reports one suCh roost in Pennsylvania that Contained over 50 birds, but 6 to 20 individuals seem to be more Common.
    [Show full text]
  • Restoring Your Degraded Grassland to Utility Meadow
    Restoring Your Degraded Grassland to Utility Meadow The author of this Restoration Guide is Laura Phillips-Mao, University of Minnesota. Steve Chaplin, MN/ND/SD Chapter of The Nature Conservancy, administered the project and helped with production. Marybeth Block, Minnesota Department of Natural Resources, provided review and editorial comments. Susan Galatowitsch, University of Minnesota, contributed to an earlier version of this guide. ©The Nature Conservancy January 1, 2017 Funding for the development of this restoration guide was provided by the Minnesota Environment and Natural Resources Trust Fund as recommended by the Legislative-Citizen Commission on Minnesota Resources (LCCMR) through grant LCCMR092C. The Trust Fund is a permanent fund constitutionally established by the citizens of Minnesota to assist in the protection, conservation, preservation, and enhancement of the state’s air, water, land, fish, wildlife, and other natural resources. Currently 40% of net Minnesota State Lottery proceeds are dedicated to building the Trust Fund and ensuring future benefits for Minnesota’s environment and natural resources. Additional funding for the update and redesign of the guide was provided by a Working Lands Initiative grant from the Minnesota Department of Natural Resources. Cover photo taken at Pankratz Prairie by Justin Meissen. Restoring Your Compatible land uses include: Conservation grazing using cattle or bison1 Degraded Grassland to Hay production Commercial seed harvest “Utility Meadow” Recreational activities such as hunting Conservation benefits include improved water In this guide, you will learn the basic steps to quality, flood control, and habitat for birds, restore a degraded grassland of native and animals and insects. Utility meadow can also invasive species to a utility meadow.
    [Show full text]
  • Species Rich Grassland Management and Creation
    species rich grassland management and creation Photo: David Chamberlain Why are wildflower grasslands important? Wildflower meadows are one of the key habitats needed by greater to hear the echo of their call in order to find their way around, they horseshoe bats in the landscape around their summer maternity require navigational features, such as hedges or trees, within a few roosts. Wildflower grasslands support huge numbers of insects which metres of their feeding grounds. bats feed upon. They particularly need moths, cockchafers, craneflies and other large bugs found in wildflower grasslands. Around 2% of this Wildflower grasslands, grazed with cattle after a hay cut, add even type of habitat remains compared to a century ago and this is mirrored more benefit both to the structure and diversity of the meadow and to in a decline in the range and numbers of greater horseshoe bats. the bats. The dung beetles which feed on cow dung are particularly important to young greater horseshoe bats. If cattle are not available, Small traditional meadows surrounded by tall bushy hedgerows are then grazing by other livestock types is still beneficial, but their dung perfect for bats. Greater horseshoe bats have a very high frequency may not support the same quantities of dung beetles. call, which is both quiet and directional. This means that it disappears rapidly if it has nothing to bounce back from. Because they need www.devonbatproject.org A brief history of meadows Meadow plants have co-evolved with traditional agriculture over Speak to an advisor for specific thousands of years. Initially hay cuts were taken over the course of information on your land the summer as it was a long and tiring process.
    [Show full text]
  • Biomass and Activity in Temperate Steppe Soils
    UC Irvine UC Irvine Previously Published Works Title Precipitation regime drives warming responses of microbial biomass and activity in temperate steppe soils Permalink https://escholarship.org/uc/item/5qp6f8sg Journal Biology and Fertility of Soils, 52(4) ISSN 0178-2762 Authors Liu, W Allison, SD Xia, J et al. Publication Date 2016-05-01 DOI 10.1007/s00374-016-1087-7 Peer reviewed eScholarship.org Powered by the California Digital Library University of California AUTHOR'S PROOF! 53 Foot note The online version of this article (doi:10.1007/s00374-016-1087-7) contains information supplementary material, which is available to authorized users. Electronic supplementary material Figure S1 The relationships between annual precipitation and aboveground net primary productivity (ANPP) and microbial properties including soil microbial biomass C (MBC; a, b), N (MBN; c, d), and respiration (MR; e, f) for all replicates across sites and years. (DOCX 103 kb) Figure S2 Warming-induced changes in (a) aboveground net primary productivity (ANPP) and (b) belowground net primary productivity (BNPP) in the desert, typical, and meadow steppes in 2006, 2007, 2008, and 2009. (DOCX 38 kb) Figure S3 Relationships between soil temperature (T) and soil microbial biomass C (MBC; a, b, c), N (MBN; d, e, f), and respiration (MR; g, h, i) across the 3 sites in each year. (DOCX 96 kb) AUTHOR'S PROOF! JrnlID 374_ArtID 1087_Proof# 1 - 16/01/2016 Biol Fertil Soils DOI 10.1007/s00374-016-1087-7 1 3 ORIGINAL PAPER 2 4 Precipitation regime drives warming responses of microbial 5 biomass and activity in temperate steppe soils 1 2,3 4 1 5 6 Weixing Liu & Steven D.
    [Show full text]
  • The Food of the Imperial Eagle (Aquila Heliaca) in Slovakia
    Slovak Rapt J 2007, 1: 1 – 18 © Raptor Protection of Slovakia (RPS) The Food of the Imperial Eagle (Aquila heliaca) in Slovakia Potrava orla kráľovského (Aquila heliaca) na Slovensku Jozef CHAVKO, Štefan DANKO, Ján OBUCH & Jozef MIHÓK _____________________________________________________________________________________________________________ Chavko J, Danko Š, Obuch J & Mihók J 2007: The Food of the Imperial Eagle (Aquila heliaca) in Slovakia. Slovak Rapt J, 1: 1-18. Abstract: In this work we assess the data on the food of the Imperial Eagle (Aquila heliaca) in two separate nest- ing populations: one in Western Slovakia (21 pairs), the other in Eastern Slovakia (30 pairs). In Western Slovakia between 1978 and 2005 we recorded a total of 562 food items, consisting of 33 species of animal. The species predominantly featuring in the food were the brown hare Lepus europaeus (40.2%), common pheasant Phasianus colchicus (17.3%), feral pigeon Columba livia domestica (11.7%) and the common hamster Cricetus cricetus (11.6%). In Eastern Slovakia between 1971 and 2005 we identified a total of 524 food items, made up of 30 animal species with slightly varying predominance of the same principal kinds of prey: L. europaeus (29.0%), C. cricetus (27.7%), P. colchicus (8.4%) and Columba sp. (8.2%). Imperial Eagles nesting in Slovakia are affected by the consequences of a marked reduction in population density of steppe-type rodents, especially ground squirrels (Spermophilus citellus) and hamsters (C. cricetus) and have become dependent for their food mainly on the preva- lence of other small animals (L. europaeus, P. colchicus) and pigeons (C. livia domestica).
    [Show full text]
  • A Guide to Climate-Smart Meadow Restoration in the Sierra Nevada and Southern Cascades
    1 A guide to climate-smart meadow restoration in the Sierra Nevada and southern Cascades Version 1.0, May 2019 Marian E. Vernon, Brent R. Campos, and Ryan D. Burnett Point Blue Contribution Number 2232 2 Table of Contents Introduction .................................................................................................................................................. 4 Handbook Outline ..................................................................................................................................... 5 Section I: Conducting a climate vulnerability assessment ............................................................................ 5 Step 1: Define objectives and desired outcomes. .................................................................................... 6 Step 2: Gather relevant data ..................................................................................................................... 7 Step 3: Assess climate vulnerabilities ..................................................................................................... 12 Step 4: Identify climate-smart restoration actions and adaptation approaches. ................................... 12 Section II: A vulnerability assessment for Sierra meadows ........................................................................ 14 Desired Outcome: Functional Meadow Hydrology ................................................................................ 15 Desired Outcome: Good Water Quality .................................................................................................
    [Show full text]
  • The Garden View April 11 April 12 Add Variety to Your Home’S Yard and (While Supplies Last) • Hanging Basket Extravaganza Garden
    Calendar of Events DIY Creation Station Container gardening is a great way to , 9 am-5 pm and , Noon-5 pm the garden view April 11 April 12 add variety to your home’s yard and (while supplies last) • Hanging Basket Extravaganza garden. By mixing colors, heights MEADOW VIEW GROWERS • SPRING 2015 Buy one hanging basket, get one free. Limit of four free and containers, you can create unique pieces to last all summer. Mid-April - May • Help Stomp Out Alzheimer’s www.meadowview.com • 937.845.0093 Meadow View has a DIY (do-it-yourself) Buy select planted purple pots and half the proceeds go to the Just north of I-70 on SR 235 in New Carlisle potting station during regular business Alzheimer’s Association (while supplies last) hours in April and May. All garden lovers are April 18 • Tool Sharpening with Rick welcome to come play in the dirt at MVG and leave the mess Tool Sharpening (hand-held only) 1-4 pm $2/tool. Limit 3/person behind. Whether you’ve been planting for years or you’re just A Sustainable Future April 24 • National Arbor Day 20% Off All Trees beginning to garden, our Creation Station is a great place to start. We provide the supplies. You can bring your own pot or How Meadow View Growers April 24-26 • Perennial Quart Sale Buy 3 quarts, get 1 quart free purchase one from our huge selection. Buy 1 flat, get 1 flat 50% May 1-3 • Pansy and Petunia Flat sale Stop by our Creation Station and get your hands dirty while is Eco-Friendly off and Wave petunia value paks ($2 off) saving time and money.
    [Show full text]
  • Mountain Meadows--Here Today, Gone Tomorrow? Meadow Science
    PNW Pacific Northwest Research Station I NSIDE The Where and Why of Meadows .............................. 2 Evidence of Change ..................................................... 3 Consequences for Meadow Ecosystems .................. 3 A Restoration Experiment........................................... 4 FINDINGS issue ninety four / june 2007 “Science affects the way we think together.” Lewis Thomas MOUNTAIN MEADOWS—HERE TODAY, GONE TOMORROW? MEADOW SCIENCE AND RESTORATION IN S UMMA R Y Mountain meadows in the Pacific Northwest are patches of remarkable biological diversity. Lush, forb-, grass-, and shrub-dominated communities attract rich assemblages of arthropods, support diverse communities of birds, and provide habitat for small mammals and other wildlife. Recent encroachment by conifers has reduced the extent and ecological integrity of meadows, with consequences for their biota, scenic values, and recreational use. Using a diversity of approaches, researchers and managers are attempting to unravel the causes and consequences of encroachment and the potential for maintaining or restoring these important habitats. James A. Lutz Using historical aerial photography, Conifer invasions into meadows sometimes take the form of tree islands. researchers at the PNW Research Station laboratory in Corvallis, Oregon, performed “How does the meadow flower mountain meadows are precious patches retrospective analyses of meadow extent in a its bloom unfold? Because of diversity, havens of distinction. portion of the western Cascades. They found that half of the nonforested areas present in the lovely little flower is Ecologists are quick to confirm that 1946 now support conifers, particularly where free down to its root, and instinct: Cascade meadows are biological fire occurred in adjacent forest during the in that freedom bold.” hotspots. They are home to unique communities of plants that cannot survive previous century.
    [Show full text]