Grassland Ecosystem Guidelines Landscape Interpretation for Planners and Managers Citation: SANBI
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Tulbagh Renosterveld Project Report
BP TULBAGH RENOSTERVELD PROJECT Introduction The Cape Floristic Region (CFR) is the smallest and richest floral kingdom of the world. In an area of approximately 90 000km² there are over 9 000 plant species found (Goldblatt & Manning 2000). The CFR is recognized as one of the 33 global biodiversity hotspots (Myers, 1990) and has recently received World Heritage Status. In 2002 the Cape Action Plan for the Environment (CAPE) programme identified the lowlands of the CFR as 100% irreplaceable, meaning that to achieve conservation targets all lowland fragments would have to be conserved and no further loss of habitat should be allowed. Renosterveld , an asteraceous shrubland that predominantly occurs in the lowland areas of the CFR, is the most threatened vegetation type in South Africa . Only five percent of this highly fragmented vegetation type still remains (Von Hase et al 2003). Most of these Renosterveld fragments occur on privately owned land making it the least represented vegetation type in the South African Protected Areas network. More importantly, because of the fragmented nature of Renosterveld it has a high proportion of plants that are threatened with extinction. The Custodians of Rare and Endangered Wildflowers (CREW) project, which works with civil society groups in the CFR to update information on threatened plants, has identified the Tulbagh valley as a high priority for conservation action. This is due to the relatively large amount of Renosterveld that remains in the valley and the high amount of plant endemism. The CAPE program has also identified areas in need of fine scale plans and the Tulbagh area falls within one of these: The Upper Breede River planning domain. -
Comparison of Extent and Transformation of South Africa's
View metadata, citation and similar papers at core.ac.uk brought to you by CORE provided by South East Academic Libraries System (SEALS) Research in Action South African Journal of Science 97, May/June 2001 179 remote sensing applications in South Comparison of extent and Africa. This is a hierarchical framework designed to suit South African conditions, transformation of South Africa’s and incorporates known land-cover types that can be identified in a consistent woodland biome from two national and repetitive manner from high- resolution satellite imagery such as Land- databases sat TM and SPOT.The ‘natural’vegetation classes are based on broad, structural M.W. Thompsona*, E.R. Vinka, D.H.K. Fairbanksb,c, A. Ballancea types only, and are not intended to be and C.M. Shackletona,d equivalent to a floristic or ecological vege- tation classification. It is important to understand that a HE RECENT COMPLETION OF THE SOUTH Fairbanks et al.5 combination of both the NLC database’s TAfrican National Land-Cover Database This paper compares the distribution ‘Woodland’ and ‘Thicket, Bushland, and the Vegetation Map of South Africa, and location of woodland and bushveld- Bush-Clump & Tall Fynbos’ land-cover Swaziland and Lesotho, allows for the first type vegetation categories defined within classes were used in the comparison with time a comparison to be made on a national scale between the current and potential the NLC data, and the equivalent the DEAT defined ‘Savanna Biome’. The distribution of ‘natural’ vegetation resources. ‘Savanna Biome’ class defined within the inclusion of the NLC’s ‘Thicket, Bushland This article compares the distribution and DEAT’s ‘VegetationMap’ data. -
National Forests Act: List of Protected Tree Species
6 No. 37037 GOVERNMENT GAZETTE, 22 NOVEMBER 2013 GOVERNMENT NOTICES GOEWERMENTSKENNISGEWINGS DEPARTMENT OF AGRICULTURE, FORESTRY AND FISHERIES DEPARTEMENT VAN LANDBOU, BOSBOU EN VISSERYE No. 877 22 November 2013 NOTICE OFOF THETHE LISTLIST OFOF PROTECTEDPROTECTED TREE TREE SPECIES SPECIES UNDER UNDER THE THE NATIONAL NATIONAL FORESTS ACT, 19981998 (ACT(ACT NO No. 84 84 OF OF 1998) 1998) By virtue of powers vested in me under Section 15(3) of the National Forests Act, 1998, I, Tina Joemat-Pettersson, Minister of Agriculture, Forestry and Fisheries hereby publish a list of all protected trees belonging to a particular species under Section 12(1) (d) set out in Schedule below. The effect of this declaration is that in terms of Section 15(1) of the National Forests Act, 1998, no person may cut, disturb, damage or destroy any protected tree or possess, collect, remove, transport, export, purchase, sell, donate or in any other manner acquire or dispose of any protected tree or any forest product derived from a protected tree, except under a licence or exemption granted by the Minister to an applicant and subject to such period and conditions as may be stipulated. Contravention of this declaration is regarded as a first category offence that may result in a person who is found guilty of being sentenced to a fine or imprisonment for a period up to three years, or to both a fine and imprisonment. SCHEDULE A / BYLAE A Botanical Name English Other Common Names National Common Afrikaans (A), Northern SothoTree Names (NS),SouthernSotho (S),Number Tswana (T), Venda (V), Xhosa (X), Zulu (Z) Acacia erioloba Camel thorn Kameeldoring (A) / Mogohlo (NS) / 168 Mogotlho (T) Acacia haematoxylon Grey camel thorn Vaalkameeldoring (A) / Mokholo (T) 169 Adansonia digitata Baobab Kremetart (A) /Seboi (NS)/ Mowana 467 (T) Afzelia quanzensis Pod mahogany Peulmahonie (A) / Mutokota (V) / 207 lnkehli (Z) Balanites subsp. -
Maloti-Drakensberg Park, Lesotho & South Africa
IUCN World Heritage Outlook: https://worldheritageoutlook.iucn.org/ Maloti-Drakensberg Park - 2020 Conservation Outlook Assessment Maloti-Drakensberg Park 2020 Conservation Outlook Assessment SITE INFORMATION Country: Lesotho, South Africa Inscribed in: 2000 Criteria: (i) (iii) (vii) (x) The Maloti-Drakensberg Park is a transboundary site composed of the uKhahlamba Drakensberg National Park in South Africa and the Sehlathebe National Park in Lesotho. The site has exceptional natural beauty in its soaring basaltic buttresses, incisive dramatic cutbacks, and golden sandstone ramparts as well as visually spectacular sculptured arches, caves, cliffs, pillars and rock pools. The site's diversity of habitats protects a high level of endemic and globally important plants. The site harbors endangered species such as the Cape vulture (Gyps coprotheres) and the bearded vulture (Gypaetus barbatus). Lesotho’s Sehlabathebe National Park also harbors the Maloti minnow (Pseudobarbus quathlambae), a critically endangered fish species only found in this park. This spectacular natural site contains many caves and rock-shelters with the largest and most concentrated group of paintings in Africa south of the Sahara. They represent the spiritual life of the San people, who lived in this area over a period of 4,000 years. © UNESCO SUMMARY 2020 Conservation Outlook Finalised on 01 Dec 2020 SIGNIFICANT CONCERN The conservation outlook for Maloti-Drakensberg Park is of significant concern. The EKZNW management staff are highly dedicated and experienced and there is also significant appreciation for the values of the Maloti Drakensberg by communities living nearby as evidenced, for example, by the vehemently strong opposition to the possibility of oil and gas exploration in the area. -
CHAPTER 1: Introduction 1
University of Pretoria etd, Wilson K A (2006) Status and distribution of cheetah outside formal conservation areas in the Thabazimbi district, Limpopo province by Kelly-Anne Wilson Submitted in partial fulfilment for the requirements for the degree Magister Scientiae in Wildlife Management Centre for Wildlife Management Faculty of Natural and Agricultural Sciences University of Pretoria Pretoria Supervisor: Prof. J. du P. Bothma Co-supervisor: Prof. G. H. Verdoorn February 2006 University of Pretoria etd, Wilson K A (2006) STATUS AND DISTRIBUTION OF CHEETAH OUTSIDE FORMAL CONSERVATION AREAS IN THE THABAZIMBI DISTRICT, LIMPOPO PROVINCE by Kelly-Anne Wilson Supervisor: Prof. Dr. J. du P. Bothma Co-supervisor: Prof. Dr. G. H. Verdoorn Centre for Wildlife Management Faculty of Natural and Agricultural Sciences University of Pretoria Magister Scientiae (Wildlife Management) ABSTRACT The current status of the cheetah Acinonyx jubatus outside formal conservation areas in South Africa is undetermined. The largest part of the cheetah population in South Africa occurs on cattle and wildlife ranches. Conflict between cheetahs and landowners is common and cheetahs are often persecuted. Cheetah management and conservation efforts are hampered as little data are available on the free-roaming cheetah population. A questionnaire survey was done in the Thabazimbi district of the Limpopo province to collect data on the status and distribution of cheetahs in the district and on the ranching practices and attitudes of landowners. By using this method, a population estimate of 42 – 63 cheetahs was obtained. Camera trapping was done at a scent-marking post to investigate the marking behaviour of cheetahs. Seven different cheetahs were identified marking at one specific tree. -
Science and Stewardship to Protect and Sustain Wilderness Values
Using Biodiversity Stewardship as a Means to Secure the Natural Wild Values on Communal Land in South Africa Kevin McCann, Dr Roelie Kloppers, and Dr Andrew Venter Abstract—South Africa is one of the most biodiversity-rich coun- These voluntary Biodiversity Stewardship agreements are charac- tries in the world, with much valuable biodiversity situated on a terised by innovative, pro-poor green enterprise-based approaches to range of different land tenure types, including state, private and sustainable development and the conservation of biodiversity. They communal land. Despite this, these wild lands are being lost at an aim to create a green economy where the conservation of ecosystems unprecedented rate, with the resultant loss of natural areas and and biodiversity is the foundation of sustainable development and associated ecosystem services. The challenge lies in the need to where a closer alignment of environmental and economic systems protect the unique biodiversity, by integrating the development is imperative, ensuring direct community benefit through improved needs of poverty-stricken communities with the need to secure the natural resource management. remaining natural wild places, and thereby secure the very areas on which these communities rely for their daily requirements (water, firewood, medicinal plants). Biodiversity Stewardship is increasingly becoming the principal strategy to secure land, in favour of more traditional methods such Introduction ______________________ as land acquisition. This mechanism recognises landowners as cus- As a developing country that needs to reduce poverty lev- todians of their land, and promotes and supports the wise use and els and ensure sustainable livelihoods for its people, South management of natural resources and biodiversity, through the form Africa faces critical challenges relating to the need to protect of voluntary legal agreements, thereby making rural landowners biodiversity and at the same time implement programmes effective “stewards” of their land. -
Lesotho Fourth National Report on Implementation of Convention on Biological Diversity
Lesotho Fourth National Report On Implementation of Convention on Biological Diversity December 2009 LIST OF ABBREVIATIONS AND ACRONYMS ADB African Development Bank CBD Convention on Biological Diversity CCF Community Conservation Forum CITES Convention on International Trade in Endangered Species CMBSL Conserving Mountain Biodiversity in Southern Lesotho COP Conference of Parties CPA Cattle Post Areas DANCED Danish Cooperation for Environment and Development DDT Di-nitro Di-phenyl Trichloroethane EA Environmental Assessment EIA Environmental Impact Assessment EMP Environmental Management Plan ERMA Environmental Resources Management Area EMPR Environmental Management for Poverty Reduction EPAP Environmental Policy and Action Plan EU Environmental Unit (s) GA Grazing Associations GCM Global Circulation Model GEF Global Environment Facility GMO Genetically Modified Organism (s) HIV/AIDS Human Immuno Virus/Acquired Immuno-Deficiency Syndrome HNRRIEP Highlands Natural Resources and Rural Income Enhancement Project IGP Income Generation Project (s) IUCN International Union for Conservation of Nature and Natural Resources LHDA Lesotho Highlands Development Authority LMO Living Modified Organism (s) Masl Meters above sea level MDTP Maloti-Drakensberg Transfrontier Conservation and Development Project MEAs Multi-lateral Environmental Agreements MOU Memorandum Of Understanding MRA Managed Resource Area NAP National Action Plan NBF National Biosafety Framework NBSAP National Biodiversity Strategy and Action Plan NEAP National Environmental Action -
Introduction Premier Hotel Himeville Arms
World Class Africa Make your reservation today at Central Reservations: 086 111 5555 | www.premierhotels.co.za PREMIER HOTELS • PREMIER RESORTS • SPLENDID INNS BY PREMIER EXPRESS INNS BY PREMIER • EAST LONDON INTERNATIONAL CONVENTION CENTRE Introduction Premier Hotel Himeville Arms - Gateway To Lesotho And Southern Drakensberg. Premier Hotel Himeville Arms is located in the picturesque Drakensberg Town of Himeville with its tree lined avenues and friendly country people. Himeville is 12km from Sani Pass with all that it offers. Adventure, running, cycling and 4X4 Adventure. The Premier Hotel Himeville Arms opened in 1904 and still reflects the 19th Century not only in the building and furniture but also in the friendliness and warm welcome that the staff provides all their Guests. The ideal stop off for overnight accommodation or to spend the evening in the atmospheric pub with wonderful menu. The Premier Hotel Himeville Arms is 3km from the Himeville airstrip and 5km from Underberg and all the local attractions. Premier Hotel Himeville Arms • Southern Drakensberg • Kwa-Zulu Natal • South Africa Overview LOCATION ACCOMMODATION 10 Standard Rooms Double or twin beds | En-suite bathroom Nestled below the towering Drakensberg mountains, the Premier Hotel Telephone | Hairdryer | Tea & Coffee Making Himeville Arms, with its Old English charm and decor opened in 1904 and Facilities | Select DSTV Bouquet Suites still reflects its 20th Century origins. From the “ye olde English” architecture 4 Private Sitting Room | Queen, Double & Sleeper Couch or 2 Three-quarter beds with and antique furniture to the modern day conveniences and friendly staff – sleeper couch | En-suite bathroom Premier Hotel Himeville Arms provides a journey and a destination. -
Fire Management
FACT SHEET The Landowner’s Guide to FIRE MANAGEMENT eriodic natural fires have always occurred in fynbos and probably in renosterveld systems too. Many plants actually need fires to reproduce and ensure their long-term survival. The Pchallenge now is to use fire in a fragmented and highly modified modern landscape to ensure the survival of all plant and animal species that live in the landscape. Although fynbos is a fire-adapted system, just one or two inappropriate fires at the wrong time of year or wrong frequency, can cause the local extinction of many species. The most important use of fire for conservation management is to maintain viable populations of all existing plant and animal species. The use of fire to achieve other management objectives should always take this into account. These may include: reduction in fuel load to prevent unmanageable wildfires, the control of invasive alien plants, increase in water yield from catchments, promoting desirable plants for the flower picking industry, or improving grazing. Principles of Fire Management Frequency can contain a high proportion of grasses, which are fast- growing and highly flammable, renosterveld can be The interval between fires should largely be deter- burned more frequently than fynbos, possibly every mined by the growth rate of existing plants. No fire three to 10 years. However, renosterveld is far less should be permitted in fynbos until at least 50% dependent on fire than fynbos. of the population of the slowest-maturing species in an area have flowered for at least Light is important for bulb flowering and the germina- three successive seasons. -
The Grassland Vegetation of the Low Drakensberg Escarpment in the North-Western Kwazulu-Natal and North-Eastern Orange Free State Border Area
S. Afr. J. Bot.. 1995.61(1): 9-17 9 The grassland vegetation of the Low Drakensberg escarpment in the north-western KwaZulu-Natal and north-eastern Orange Free State border area C.M. Smit, G.J. Bredenkamp' and N. van Rooyen Department of Botany, University of Pretoria, 0002 Pretoria. Republic of South Africa Received: 17 Augll.u /99-1; revised I J October 1994 This study of the grasslands of the Low Drakenberg escarpment in the Newcastle-Meme] area forms part of the Grassland Biome Project. The 44 releves compiled in the Fa land type which represents the escarpment. were numer ically classified (TWINSPAN), and the results were refined by Braun-Blanquet procedures. The analyses revealed nine plant communities. A hierarchical classification, description and ecological interpretation of the nine plant communities are presented. Hi erdie ondersoek van die grasvelde van die Lae Drakensberg platorand in die Newcastle-Memel gebied maak deel uit van die Grasveldbioomprojek. Die 44 rei eves wat saamgestel is in die Fa landtipe wat die platorand verleen woordig, is numeries geklassifiseer (TWINSPAN) en die resultate is met behulp van Braun-Blanquet prosedures verfyn. Nege plantgemeenskappe is onderskei. 'n Hierargiese klassifikasie, beskrywing en ekologiese interpretasie van die nege plantgemeenskappe word aangebied. Keywords: Braun-8lanquet procedures, eastern escarpment, ecological in terpretation, Fa land type, grassland, vegetation classification . • To whom correspondence should be addressed. Introduction have been completed in the north-eastern Transvaal by Deall ct The Drakensberg Range forms part of the Great Escarpmenl at al. (1989) and Matthews et al. (1991. 1992a & 1992b). in the the eastern edge of the interi or plateau of southern Africa (Par eastern Oran ge Free State by Du Preez and Bredenkamp (1991), tridge & Maud 1987). -
Umlalazi Strategic Planning Session
UMLALAZI STRATEGIC PLANNING SESSION INTEGRATED DEVELOPMENT PLANNING Lizette Dirker IDP Coordination Business Unit INFORMANTS OF THE IDP SOUTH AFRICAN PLANNING SYSTEMS National Provincial Local District wide PGDS Vision 2030 DGDP (Vision 2035) (Vision 2035) National IDP PGDP Development 5 years Plan National Provincial Municipal Planning Planning Council Commission Commission WARD BASED SDGs SDGs PLANS “KZN as a prosperous Province with healthy, secure and skilled population, living in dignity and harmony, acting as a gateway to Africa and the World” Sustainable Development Goals AGENDA 2063 50 Year Vision • Agenda 2063 is a strategic framework for the socio-economic transformation of the continent over the next 50 years. It builds on, and seeks to accelerate the implementation of past and existing continental initiatives for growth and sustainable development Adopted in January 2015 • Adopted in January 2015, in Addis Ababa, Ethiopia by the 24th African Union (AU) Assembly of Heads of State and Government 10 Year implementation cycle • Five ten year implementation plan – the first plan 2014-2023 1. A prosperous Africa based on inclusive growth and sustainable 5. An Africa with a strong cultural development identity, common heritage, shared values and ethics 2. An integrated continent, politically united and based on the ideals of Pan-Africanism and the 6. An Africa whose development vision of Africa’s Renaissance is people-driven, relying on the potential of African people, especially its women and youth, and caring for children 3. An Africa of good governance, democracy, respect for human rights, justice and the rule of law 7. Africa as a strong, united and influential global player and partner 4. -
Arctic and Boreal Plant Species Decline at Their Southern Range Limits in the Rocky Mountains
Ecology Letters, (2017) 20: 166–174 doi: 10.1111/ele.12718 LETTER Arctic and boreal plant species decline at their southern range limits in the Rocky Mountains Abstract Peter Lesica1,2* and Climate change is predicted to cause a decline in warm-margin plant populations, but this hypoth- Elizabeth E. Crone3 esis has rarely been tested. Understanding which species and habitats are most likely to be affected is critical for adaptive management and conservation. We monitored the density of 46 populations representing 28 species of arctic-alpine or boreal plants at the southern margin of their ranges in the Rocky Mountains of Montana, USA, between 1988 and 2014 and analysed population trends and relationships to phylogeny and habitat. Marginal populations declined overall during the past two decades; however, the mean trend for 18 dicot populations was À5.8% per year, but only À0.4% per year for the 28 populations of monocots and pteridophytes. Declines in the size of peripheral populations did not differ significantly among tundra, fen and forest habitats. Results of our study support predicted effects of climate change and suggest that vulnerability may depend on phylogeny or associated anatomical/physiological attributes. Keywords arctic-alpine plants, boreal plants, climate change, fens, marginal populations, peripheral popula- tions, range margins, Rocky Mountains. Ecology Letters (2017) 20: 166–174 2009; Sexton et al. 2009; Brusca et al. 2013), which suggests INTRODUCTION that in some cases climate does not determine a species’ range. Climate of the earth is changing at an unprecedented rate Nonetheless, most plant ecologists believe that climate is an (Jackson & Overpeck 2000; IPCC 2013) and is predicted to important factor determining geographic range limits.