Pdf Bamford, A.J., Diekmann, M., Monadjem, A., Mendelsohn, J., 2007
Total Page:16
File Type:pdf, Size:1020Kb
Load more
Recommended publications
-
Grassland & Shrubland Vegetation
Grassland & Shrubland Vegetation Missoula Draft Resource Management Plan Handout May 2019 Key Points Approximately 3% of BLM-managed lands in the planning area are non-forested (less than 10% canopy cover); the other 97% are dominated by a forested canopy with limited mountain meadows, shrublands, and grasslands. See table 1 on the following page for a break-down of BLM-managed grassland and shrubland in the planning area classified under the National Vegetation Classification System (NVCS). The overall management goal of grassland and shrubland resources is to maintain diverse upland ecological conditions while providing for a variety of multiple uses that are economically and biologically feasible. Alternatives Alternative A (1986 Garnet RMP, as Amended) Maintain, or where practical enhance, site productivity on all public land available for livestock grazing: (a) maintain current vegetative condition in “maintain” and “custodial” category allotments; (b) improve unsatisfactory vegetative conditions by one condition class in certain “improvement” category allotments; (c) prevent noxious weeds from invading new areas; and, (d) limit utilization levels to provide for plant maintenance. Alternatives B & C (common to all) Proposed objectives: Manage uplands to meet health standards and meet or exceed proper functioning condition within site or ecological capability. Where appropriate, fire would be used as a management agent to achieve/maintain disturbance regimes supporting healthy functioning vegetative conditions. Manage surface-disturbing activities in a manner to minimize degradation to rangelands and soil quality. Mange areas to conserve BLM special status species plants. Ensure consistency with achieving or maintaining Standards of Rangeland Health and Guidelines for Livestock Grazing Management for Montana, North Dakota, and South Dakota. -
Tropical Deciduous Forests and Savannas
2/1/17 Tropical Coastal Communities Relationships to other tropical forest systems — specialized swamp forests: Tropical Coastal Forests Mangrove and beach forests § confined to tropical and & subtropical zones at the interface Tropical Deciduous Forests of terrestrial and saltwater Mangrove Forests Mangrove Forests § confined to tropical and subtropical § stilt roots - support ocean tidal zones § water temperature must exceed 75° F or 24° C in warmest month § unique adaptations to harsh Queensland, Australia environment - convergent Rhizophora mangle - red mangrove Moluccas Venezuela 1 2/1/17 Mangrove Forests Mangrove Forests § stilt roots - support § stilt roots - support § pneumatophores - erect roots for § pneumatophores - erect roots for O2 exchange O2 exchange § salt glands - excretion § salt glands - excretion § viviparous seedlings Rhizophora mangle - red mangrove Rhizophora mangle - red mangrove Xylocarpus (Meliaceae) & Rhizophora Mangrove Forests Mangrove Forests § 80 species in 30 genera (20 § 80 species in 30 genera (20 families) families) § 60 species OW& 20 NW § 60 species OW& 20 NW (Rhizophoraceae - red mangrove - Avicennia - black mangrove; inner Avicennia nitida (black mangrove, most common in Neotropics) boundary of red mangrove, better Acanthaceae) drained Rhizophora mangle - red mangrove Xylocarpus (Meliaceae) & Rhizophora 2 2/1/17 Mangrove Forests § 80 species in 30 genera (20 families) § 60 species OW& 20 NW Four mangrove families in one Neotropical mangrove community Avicennia - Rhizophora - Acanthanceae Rhizophoraceae -
Understanding the Causes of Bush Encroachment in Africa: the Key to Effective Management of Savanna Grasslands
Tropical Grasslands – Forrajes Tropicales (2013) Volume 1, 215−219 Understanding the causes of bush encroachment in Africa: The key to effective management of savanna grasslands OLAOTSWE E. KGOSIKOMA1 AND KABO MOGOTSI2 1Department of Agricultural Research, Ministry of Agriculture, Gaborone, Botswana. www.moa.gov.bw 2Department of Agricultural Research, Ministry of Agriculture, Francistown, Botswana. www.moa.gov.bw Keywords: Rangeland degradation, fire, indigenous ecological knowledge, livestock grazing, rainfall variability. Abstract The increase in biomass and abundance of woody plant species, often thorny or unpalatable, coupled with the suppres- sion of herbaceous plant cover, is a widely recognized form of rangeland degradation. Bush encroachment therefore has the potential to compromise rural livelihoods in Africa, as many depend on the natural resource base. The causes of bush encroachment are not without debate, but fire, herbivory, nutrient availability and rainfall patterns have been shown to be the key determinants of savanna vegetation structure and composition. In this paper, these determinants are discussed, with particular reference to arid and semi-arid environments of Africa. To improve our current under- standing of causes of bush encroachment, an integrated approach, involving ecological and indigenous knowledge systems, is proposed. Only through our knowledge of causes of bush encroachment, both direct and indirect, can better livelihood adjustments be made, or control measures and restoration of savanna ecosystem functioning be realized. Resumen Una forma ampliamente reconocida de degradación de pasturas es el incremento de la abundancia de especies de plan- tas leñosas, a menudo espinosas y no palatables, y de su biomasa, conjuntamente con la pérdida de plantas herbáceas. En África, la invasión por arbustos puede comprometer el sistema de vida rural ya que muchas personas dependen de los recursos naturales básicos. -
The Coastal Scrub and Chaparral Bird Conservation Plan
The Coastal Scrub and Chaparral Bird Conservation Plan A Strategy for Protecting and Managing Coastal Scrub and Chaparral Habitats and Associated Birds in California A Project of California Partners in Flight and PRBO Conservation Science The Coastal Scrub and Chaparral Bird Conservation Plan A Strategy for Protecting and Managing Coastal Scrub and Chaparral Habitats and Associated Birds in California Version 2.0 2004 Conservation Plan Authors Grant Ballard, PRBO Conservation Science Mary K. Chase, PRBO Conservation Science Tom Gardali, PRBO Conservation Science Geoffrey R. Geupel, PRBO Conservation Science Tonya Haff, PRBO Conservation Science (Currently at Museum of Natural History Collections, Environmental Studies Dept., University of CA) Aaron Holmes, PRBO Conservation Science Diana Humple, PRBO Conservation Science John C. Lovio, Naval Facilities Engineering Command, U.S. Navy (Currently at TAIC, San Diego) Mike Lynes, PRBO Conservation Science (Currently at Hastings University) Sandy Scoggin, PRBO Conservation Science (Currently at San Francisco Bay Joint Venture) Christopher Solek, Cal Poly Ponoma (Currently at UC Berkeley) Diana Stralberg, PRBO Conservation Science Species Account Authors Completed Accounts Mountain Quail - Kirsten Winter, Cleveland National Forest. Greater Roadrunner - Pete Famolaro, Sweetwater Authority Water District. Coastal Cactus Wren - Laszlo Szijj and Chris Solek, Cal Poly Pomona. Wrentit - Geoff Geupel, Grant Ballard, and Mary K. Chase, PRBO Conservation Science. Gray Vireo - Kirsten Winter, Cleveland National Forest. Black-chinned Sparrow - Kirsten Winter, Cleveland National Forest. Costa's Hummingbird (coastal) - Kirsten Winter, Cleveland National Forest. Sage Sparrow - Barbara A. Carlson, UC-Riverside Reserve System, and Mary K. Chase. California Gnatcatcher - Patrick Mock, URS Consultants (San Diego). Accounts in Progress Rufous-crowned Sparrow - Scott Morrison, The Nature Conservancy (San Diego). -
Edition 2 from Forest to Fjaeldmark the Vegetation Communities Highland Treeless Vegetation
Edition 2 From Forest to Fjaeldmark The Vegetation Communities Highland treeless vegetation Richea scoparia Edition 2 From Forest to Fjaeldmark 1 Highland treeless vegetation Community (Code) Page Alpine coniferous heathland (HCH) 4 Cushion moorland (HCM) 6 Eastern alpine heathland (HHE) 8 Eastern alpine sedgeland (HSE) 10 Eastern alpine vegetation (undifferentiated) (HUE) 12 Western alpine heathland (HHW) 13 Western alpine sedgeland/herbland (HSW) 15 General description Rainforest and related scrub, Dry eucalypt forest and woodland, Scrub, heathland and coastal complexes. Highland treeless vegetation communities occur Likewise, some non-forest communities with wide within the alpine zone where the growth of trees is environmental amplitudes, such as wetlands, may be impeded by climatic factors. The altitude above found in alpine areas. which trees cannot survive varies between approximately 700 m in the south-west to over The boundaries between alpine vegetation communities are usually well defined, but 1 400 m in the north-east highlands; its exact location depends on a number of factors. In many communities may occur in a tight mosaic. In these parts of Tasmania the boundary is not well defined. situations, mapping community boundaries at Sometimes tree lines are inverted due to exposure 1:25 000 may not be feasible. This is particularly the or frost hollows. problem in the eastern highlands; the class Eastern alpine vegetation (undifferentiated) (HUE) is used in There are seven specific highland heathland, those areas where remote sensing does not provide sedgeland and moorland mapping communities, sufficient resolution. including one undifferentiated class. Other highland treeless vegetation such as grasslands, herbfields, A minor revision in 2017 added information on the grassy sedgelands and wetlands are described in occurrence of peatland pool complexes, and other sections. -
Existing Vegetation Classification and Mapping
Existing Vegetation Classification and Mapping Technical Guide Version 1.0 Guide Version Classification and Mapping Technical Existing Vegetation United States Department of Agriculture Existing Vegetation Forest Service Classification and Ecosystem Management Coordination Staff Mapping Technical Guide Gen. Tech. Report WO-67 Version 1.0 April 2005 United States Department of Agriculture Existing Vegetation Forest Service Classification and Ecosystem Management Coordination Staff Mapping Technical Guide Gen. Tech. Report WO-67 Version 1.0 April 2005 Ronald J. Brohman and Larry D. Bryant Technical Editors and Coordinators Authored by: Section 1: Existing Vegetation Classification and Mapping Framework David Tart, Clinton K. Williams, C. Kenneth Brewer, Jeff P. DiBenedetto, and Brian Schwind Section 2: Existing Vegetation Classification Protocol David Tart, Clinton K. Williams, Jeff P. DiBenedetto, Elizabeth Crowe, Michele M. Girard, Hazel Gordon, Kathy Sleavin, Mary E. Manning, John Haglund, Bruce Short, and David L. Wheeler Section 3: Existing Vegetation Mapping Protocol C. Kenneth Brewer, Brian Schwind, Ralph J. Warbington, William Clerke, Patricia C. Krosse, Lowell H. Suring, and Michael Schanta Team Members Technical Editors Ronald J. Brohman National Resource Information Requirements Coordinator, Washington Office Larry D. Bryant Assistant Director, Forest and Range Management Staff, Washington Office Authors David Tart Regional Vegetation Ecologist, Intermountain Region, Ogden, UT C. Kenneth Brewer Landscape Ecologist/Remote Sensing Specialist, Northern Region, Missoula, MT Brian Schwind Remote Sensing Specialist, Pacific Southwest Region, Sacramento, CA Clinton K. Williams Plant Ecologist, Intermountain Region, Ogden, UT Ralph J. Warbington Remote Sensing Lab Manager, Pacific Southwest Region, Sacramento, CA Jeff P. DiBenedetto Ecologist, Custer National Forest, Billings, MT Elizabeth Crowe Riparian/Wetland Ecologist, Deschutes National Forest, Bend, OR William Clerke Remote Sensing Program Manager, Southern Region, Atlanta GA Michele M. -
7. Shrubland and Young Forest Habitat Management
7. SHRUBLAND AND YOUNG FOREST HABITAT MANAGEMENT hrublands” and “Young Forest” are terms that apply to areas Shrubland habitat and that are transitioning to mature forest and are dominated by young forest differ in “Sseedlings, saplings, and shrubs with interspersed grasses and forbs (herbaceous plants). While some sites such as wetlands, sandy sites vegetation types and and ledge areas can support a relatively stable shrub cover, most shrub communities in the northeast are successional and change rapidly to food and cover they mature forest if left unmanaged. Shrub and young forest habitats in Vermont provide important habitat provide, as well as functions for a variety of wildlife including shrubland birds, butterflies and bees, black bear, deer, moose, snowshoe hare, bobcat, as well as a where and how they variety of reptiles and amphibians. Many shrubland species are in decline due to loss of habitat. Shrubland bird species in Vermont include common are maintained on the species such as chestnut-sided warbler, white-throated sparrow, ruffed grouse, Eastern towhee, American woodcock, brown thrasher, Nashville landscape. warbler, and rarer species such as prairie warbler and golden-winged warbler. These habitat types are used by 29 Vermont Species of Greatest Conservation Need. While small areas of shrub and young forest habitat can be important to some wildlife, managing large patches of 5 acres or more provides much greater benefit to the wildlife that rely on the associated habitat conditions to meet their life requirements. Birds such as the chestnut- sided warbler will use smaller areas of young forest, but less common species such as golden-winged warbler require areas of 25 acres or more. -
Grassland to Shrubland State Transitions Enhance Carbon Sequestration in the Northern Chihuahuan Desert
Global Change Biology Global Change Biology (2015) 21, 1226–1235, doi: 10.1111/gcb.12743 Grassland to shrubland state transitions enhance carbon sequestration in the northern Chihuahuan Desert M. D. PETRIE1 ,S.L.COLLINS1 ,A.M.SWANN2 ,P.L.FORD3 andM.E. LITVAK1 1Department of Biology, University of New Mexico, Albuquerque, New Mexico, USA, 2Department of Biology, Sevilleta LTER, University of New Mexico, Albuquerque, New Mexico, USA, 3USDA Forest Service, Rocky Mountain Research Station, Albuquerque, New Mexico, USA Abstract The replacement of native C4-dominated grassland by C3-dominated shrubland is considered an ecological state tran- sition where different ecological communities can exist under similar environmental conditions. These state transi- tions are occurring globally, and may be exacerbated by climate change. One consequence of the global increase in woody vegetation may be enhanced ecosystem carbon sequestration, although the responses of arid and semiarid ecosystems may be highly variable. During a drier than average period from 2007 to 2011 in the northern Chihuahuan À2 À1 Desert, we found established shrubland to sequester 49 g C m yr on average, while nearby native C4 grassland À À was a net source of 31 g C m 2 yr 1 over this same period. Differences in C exchange between these ecosystems were pronounced – grassland had similar productivity compared to shrubland but experienced higher C efflux via ecosys- tem respiration, while shrubland was a consistent C sink because of a longer growing season and lower ecosystem respiration. At daily timescales, rates of carbon exchange were more sensitive to soil moisture variation in grassland than shrubland, such that grassland had a net uptake of C when wet but lost C when dry. -
Response of Wildlife to Bush Thinning on the North Central Freehold Farmlands of Namibia T
Forest Ecology and Management 473 (2020) 118330 Contents lists available at ScienceDirect Forest Ecology and Management journal homepage: www.elsevier.com/locate/foreco Response of wildlife to bush thinning on the north central freehold farmlands of Namibia T Matti T. Nghikembuaa,b,c, Laurie L. Markera,b, Bruce Brewera,b, Lauri Mehtätaloc, Mark Appiahc,d, ⁎ Ari Pappinenc, a Cheetah Conservation Fund, Otjiwarongo, Namibia b CCF Bush PTY Ltd, Otijwarongo, Namibia c University of Eastern Finland, School of Forest Sciences, Joensuu Campus, Yliopistokatu 7, 80101 Joensuu, Finland d Forestry Research Institute of Ghana (CSIR-FORIG), Kumasi, Ghana ARTICLE INFO ABSTRACT Keywords: Agriculture is considered the backbone of the Namibian economy. However, bush encroachment affects ap- Bush encroachment proximately 45 million hectares of Namibian farmland and in the absence of appropriate restoration measures, Biodiversity negatively affects local biodiversity and the national economy. Bush thinning operations on three freehold farms Restoration were assessed to examine the response of local ungulates (small, medium, large) and predators (meso, large). Carrying capacity Camera traps were used to capture wildlife in bush encroached and previously thinned habitats. We hy- Overgrazing pothesized that thinning would increase the activity of small, medium, and large ungulates, meso and large Bush thinning predators, and that the magnitude of the increase in activity at thinned sites would differ among animal types. Our results revealed that the expected animal captures were not equal – small, medium, and large ungulates were common, large predators were least common; thinned areas had more expected animal captures and overall animal-treatment interactions were almost significant (p = 0.051). -
Learning the Boys' Eyes Widened and They Began to New Things, and the Colorful Pair of Socks One Ask Lots of Questions
THE CHAPARRALIAN November 16, 2009 Volume 6, Issue 3 The Chaparralian #32 Contents 3 NASCENT THOUGHTS 6 The Chaparral Habitat For Young Chaparralians Richard W. Halsey 12 Poetry of a Kindred Spirit Nancy Jordan 14 The Walking Toothbrush The Chaparralian is the quarterly journal of the California Chaparral Institute, a non-profit organization that is Bill Howell dedicated to the preservation of native shrubland ecosystems and promoting an appreciation for the natural 16 UNFOLDINGS environment through science and education. To join the Institute and receive The Chaparralian, please fill out and Cover photograph: Two boys near the mail in the slip below or join on our website. We Monkey Temple, Kathmandu, Nepal. Inside welcome unsolicited submissions to The Chaparralian. Please send to [email protected] or via post to cover photo (above left), Jaipur, India. the address below. You can find us on the web at www.californiachaparral.org All photos by Richard W. Halsey unless indicated otherwise. Editor and Publisher.......................Richard W. Halsey Please Join the California Chaparral Institute and support our research and educational efforts to help promote a better understanding of and appreciation for the remarkable biodiversity found in shrubland ecosystems, especially the chaparral! ______$35 Citizen Naturalist: The Chaparralian plus one additional benefit (check preference below). ______$55 Chaparralian: The Chaparralian plus two benefits (check preferences below). ______$100 California Grizzly Bear: The Chaparralian plus all three benefits below. _____ Signed Book: “Fire, Chaparral and Survival in Southern California” _____ DVD of the KPBS/Huell Howser’s California’s Green “Secrets of the Chaparral” show _____ Special Chaparral edition of the California Native Plant Society’s journal, Fremontia. -
4.0 Ramoelo 20032018.Indd
© University of Hamburg 2018 All rights reserved Klaus Hess Publishers Göttingen & Windhoek www.k-hess-verlag.de ISBN: 978-3-933117-95-3 (Germany), 978-99916-57-43-1 (Namibia) Language editing: Will Simonson (Cambridge), and Proofreading Pal Translation of abstracts to Portuguese: Ana Filipa Guerra Silva Gomes da Piedade Page desing & layout: Marit Arnold, Klaus A. Hess, Ria Henning-Lohmann Cover photographs: front: Thunderstorm approaching a village on the Angolan Central Plateau (Rasmus Revermann) back: Fire in the miombo woodlands, Zambia (David Parduhn) Cover Design: Ria Henning-Lohmann ISSN 1613-9801 Printed in Germany Suggestion for citations: Volume: Revermann, R., Krewenka, K.M., Schmiedel, U., Olwoch, J.M., Helmschrot, J. & Jürgens, N. (eds.) (2018) Climate change and adaptive land management in southern Africa – assessments, changes, challenges, and solutions. Biodiversity & Ecology, 6, Klaus Hess Publishers, Göttingen & Windhoek. Articles (example): Archer, E., Engelbrecht, F., Hänsler, A., Landman, W., Tadross, M. & Helmschrot, J. (2018) Seasonal prediction and regional climate projections for southern Africa. In: Climate change and adaptive land management in southern Africa – assessments, changes, challenges, and solutions (ed. by Revermann, R., Krewenka, K.M., Schmiedel, U., Olwoch, J.M., Helmschrot, J. & Jürgens, N.), pp. 14–21, Biodiversity & Ecology, 6, Klaus Hess Publishers, Göttingen & Windhoek. Corrections brought to our attention will be published at the following location: http://www.biodiversity-plants.de/biodivers_ecol/biodivers_ecol.php Biodiversity & Ecology Journal of the Division Biodiversity, Evolution and Ecology of Plants, Institute for Plant Science and Microbiology, University of Hamburg Volume 6: Climate change and adaptive land management in southern Africa Assessments, changes, challenges, and solutions Edited by Rasmus Revermann1, Kristin M. -
A Review of Potential Methods for Monitoring Rangeland Degradation in Libya Abdulsalam Al-Bukhari1,2, Stephen Hallett1* and Tim Brewer1
Al-bukhari et al. Pastoralism: Research, Policy and Practice (2018) 8:13 Pastoralism: Research, Policy https://doi.org/10.1186/s13570-018-0118-4 and Practice REVIEW Open Access A review of potential methods for monitoring rangeland degradation in Libya Abdulsalam Al-bukhari1,2, Stephen Hallett1* and Tim Brewer1 Abstract Natural and human factors exert a profound impact on the degradation of rangelands, human effects being the most significant factor in increasing the severity of deterioration. This occurs through agricultural expansion at the expense of rangelands, and with the number of domestic and wildlife animals exceeding the natural carrying capacity. This raises concerns about the ongoing sustainability of these land resources, as well as the sustainability of traditional pastoral land practices. Rangelands require effective management, which is dependent upon accurate and timely monitoring data to support the assessment of rangeland deterioration. Natural rangelands provide one of the significant pillars of support for the Libyan national economy. Despite the important role of rangeland in Libya from both economic and environmental perspectives, the vegetation cover of Libyan rangeland has changed adversely qualitatively and quantitatively over the past four decades. Ground-based observation methods are widely used to assess rangeland degradation in Libya. However, multi-temporal observations are often not integrated nor repeatable, making it difficult for rangeland managers to detect degradation consistently. Field study costs are also significantly high in comparison with their accuracy and reliability, both in terms of the time and resources required. Remote-sensing approaches offer the advantage of spanning large geographical areas with multiple spatial, spectral and temporal resolutions.