Chilcotin Meadowlands: Livestock Range and Culture
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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. -
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. -
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. -
Angling Closure – Rationale
Angling Closure – Rationale Potential Closure: Fraser River Mainstem Trout Angling Closure for Protection of Migrating Interior Fraser Steelhead (IFS) Authority: Jennifer Davis R.P.Bio., P.Ag. Director, Resource Stewardship Division Date of Document: September 19, 2019 Table of Contents. Purpose of Document ................................................................................................................................... 2 Statutory Role and Expectations. .................................................................................................................. 2 Current IFS Population: Extreme Conservation Concern. 336. .................................................................... 2 IFS Recovery Potential .................................................................................................................................. 2 Abundance Targets ....................................................................................................................................... 3 IFS Run Time. ................................................................................................................................................. 3 Threats to IFS ................................................................................................................................................ 3 IFS Economic Importance ............................................................................................................................. 4 Importance of Fisheries to BC. ..................................................................................................................... -
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. -
A Conservation Strategy Maintaining Ecological Systems And
A CONSERVATION STRATEGY MAINTAINING ECOLOGICAL SYSTEMS AND COMMUNITIES IN THE FACE OF CHANGE NOVEMBER 26, 2007 For The Cariboo-Chilcotin Beetle Action Coalition By Richard L. Case MSc RPBio R.L Case & Associates and Barbara J. Coupé RPF Arboreal Communication Services September 2007 CCBAC Interim EDWG Sector Strategies CCBAC is very pleased to make the Economic Development Working Group interim sector strategies available for use by the sector participants and stakeholders, the CCBAC working groups, the various ministries within the provincial and federal governments, and most importantly the citizens of the Cariboo-Chilcotin. CCBAC is compelled to make this information available as quickly as is possible in order to meet its objective of developing and growing the overall economic activity within the Cariboo-Chilcotin. CCBAC will identify each completed sector strategy as an ‘interim’ document through the use of this cover letter. To CCBAC this means that the interim strategy is a ‘stand alone’ document at the time of its release, and that the interim sector strategy has not been ‘integrated’ with other interim sector strategies in any manner or form. The use of the information contained within the interim sector strategy is the responsibility of the user. CCBAC does not endorse or support any specific use or proposal that uses the interim sector strategy material. CCBAC supports all interim sector strategies in principle only at this time. CCBAC intends to begin the sector strategy integration process immediately. At the conclusion of the integration process CCBAC intends to have completed a community diversification plan for the entire CCBAC area. The interim sector strategies will be an integral part of this plan. -
DISTURBANCE HISTORY and ITS INFLUENCE on DROUGHT TOLERANCE of INTERIOR DOUGLAS-FIR (Pseudotsuga Menziesii Var
DISTURBANCE HISTORY AND ITS INFLUENCE ON DROUGHT TOLERANCE OF INTERIOR DOUGLAS-FIR (Pseudotsuga menziesii var. glauca (Beissn.) Franco) IN THE CARIBOO-CHILCOTIN REGION OF BRITISH COLUMBIA, CANADA by Neil P. Thompson B.Sc., University of Maine, 2013 THESIS SUBMITTED IN PARTIAL FULFILLMENT OF THE REQUIREMENTS FOR THE DEGREE OF DOCTOR OF PHILOSOPHY IN NATURAL RESOURCE AND ENVIRONMENTAL STUDIES UNIVERSITY OF NORTHERN BRITISH COLUMBIA August 2017 © Neil P. Thompson, 2017 Abstract: Disturbance—the death of trees due to external forces such as wildfire or windstorms— drives forest stand dynamics and shapes ecosystems. Natural disturbances arising from the interaction of climate, topography, and established tree species have often occurred with some regularity, resulting in apparently perpetual renewal of particular forest structures. Minor changes in climate can have profound impacts on these disturbance regimes, breaking historically observed cycles and introducing novel stand conditions. Long-term historical baselines are critical to understanding such changes. Observational records are often inadequate, especially in western North America, where 400 year-old stands are common but reliable data are generally unavailable prior to the 20th century. I use tree ring analysis to investigate the history of Douglas-fir beetle and western spruce budworm infestations, and the influence of partial disturbances on the drought tolerance of surviving trees, developing baseline understanding of disturbance interactions in interior British Columbia. No evidence is found of any outbreaks of western spruce budworm or Douglas- fir beetle that exceed the magnitude of outbreaks in the early 21st century, suggesting that recent outbreaks represent historically high levels of insect activity. Both natural and anthropogenic partial disturbances are demonstrated to positively affect the drought tolerance of surviving trees in old-growth remnants and younger managed stands, respectively. -
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. -
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. -
Recovery Potential Assessment for Chilcotin River and Thompson River Steelhead Trout (Oncorhynchus Mykiss) Designatable Units
Canadian Science Advisory Secretariat Pacific Region Science Advisory Report 2018/050 RECOVERY POTENTIAL ASSESSMENT FOR CHILCOTIN RIVER AND THOMPSON RIVER STEELHEAD TROUT (ONCORHYNCHUS MYKISS) DESIGNATABLE UNITS Steelhead Trout image by Robert Basok. Figure 1. Major stock groups of Steelhead Trout in the Fraser River system, up stream of the Fraser Canyon. Produced by BC Ministry of Environment and Climate Change Strategy, Ecosystems Branch Context: The Chilcotin and Thompson River populations of Steelhead Trout (Oncorhynchus mykiss) were both assessed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC) in an Emergency Assessment in January 2018 based on population decline of 79% and 81% respectively over the last three generations. Fisheries and Oceans Canada (DFO) Science Branch was asked to complete a modified Recovery Potential Assessment (RPA), based on the national RPA guidance, to provide science advice to inform a Ministerial opinion on imminent threat to survival as it relates to the Emergency Assessment and a potential Governor in Council (GIC) listing decision for the addition of Steelhead Trout to Schedule 1 of the Species at Risk Act (SARA). This Science Advisory Report is from the September 20-21, 2018 regional peer review on Recovery Potential Assessment – Chilcotin River and Thompson River Steelhead Trout (Oncorhynchus mykiss) Designatable Units. Additional publications from this Regional Peer Review will be posted on the Fisheries and Oceans Canada (DFO) Science Advisory Schedule as they become available. November 2018 Recovery Potential Assessment for Chilcotin Pacific Region and Thompson River Steelhead Trout SUMMARY • This Recovery Potential Assessment (RPA) focuses on the Chilcotin and Thompson River Designatable Units (DU) of Steelhead Trout. -
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. -
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.