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2. sue milton creating a sustainable business environment linking ecology and economic development

The basis for sustainable business in the Karoo: Bringing ecological and economic issues together Sue Milton, Renu-Karoo Veld Restoration cc, PO Box 47, Prince Albert 6930
2. Karoo natural capital and its economic significance 3. Agriculture, tourism, mining: opportunities and threats 4. Ecological and economic role of a sustainability service industry Travelers between Windhoek or Gauteng and Cape Town often perceive the Karoo as a “desert”, a badland characterized by heat, dust, overgrazing and marginalized people. This was not the way in which earlier inhabitants viewed its economic and cultural role. The area supported hunter-gatherers for about one million years (Deacon and Deacon 2003; Smith 1999), nomadic herders for 2000 years (Penn 1987, Smith 1999) and has supported settled ranching for 250 years (Beinart 2003). It was once considered the economic heart of the country (Shaw 1875), but the combination of past over-exploitation of grazing that caused land degradation (Talbot 1961; Dean & Macdonald 1994; Hoffman and Ashwell 2001), and current national policies that invest preferentially in the geographical areas with the highest potential for economic growth, have led the current economic slump in the region (Nel and Hill 2008). However, despite the current local and global economic gloom, the real basis for Karoo business, the natural capital of the region, survives more or less intact. The concept of natural capital embraces all natural resources and ecosystem services that have benefits for people (Aronson et al. 2007). In this paper I will describe the richness of Karoo natural capital, the business opportunities that it provides and the ways in which Karoo business depends on it, the negative feedbacks (threats) to natural capital caused by business development, and the need for sustainability services to be supplied by the public and private sectors. 2. Karoo natural capital and its economic significance The Karoo natural capital upon which all biological, cultural and economic activity depends is water. Figure 1 illustrates how Karoo businesses depend largely upon the agricultural, tourism, mining and manufacturing sectors. Mining and manufacturing need large quantities of water as well as support from the agricultural industry (food, vegetation restoration), whereas agriculture and tourism depend both directly upon water (irrigation, laundry) and indirectly upon water through benefits derived from biodiversity (landscape, indigenous plants and animals), which in turn depend on water. Differences in the availability and spatial distribution of this limiting resource in the Succulent and Nama Karoo biomes largely determine the directions that development can take in these regions. Figure 1 showing how Karoo business depends directly and indirectly upon water and biodiversity The folded topography in the Little Karoo comprises narrow valleys and high mountains. The mountains receive rainfall from coastal air that cools as it is forced to higher altitudes, and water from the mountain tops seeps through the rock to deliver a fairly constant flow of high quality water via springs and mountain streams to the valleys. This mountain water and valley bottom accumulations of soil enable the Tanqua Karoo and the Little Karoo to support thriving deciduous fruit, olive and vegetable seed industries despite the hot arid conditions in the valley bottoms. Because of their dependence on mountain ecosystems for water, the intermountain valley businesses (agriculture and tourism) are particularly vulnerable to mismanagement of fynbos vegetation in the mountains where fires that are too hot or too frequent can result in floods, droughts and reduced water quality. In contrast with the folded belt of the Succulent Karoo, northern Namaqualand, the Richterveld and the Nama Karoo are largely dependent upon ground water. Topography is largely flat and soil shallow, actors that limit potential for arable agriculture. Major threats to availability of the ground water that supports agriculture and tourism are declining quality, caused by rapid extraction, climate change that predicts a reduction of winter rainfall in northern and western Namaqualand, and by groundwater contamination through activities such as mining. The Succulent Karoo is a global biodiversity hotspot, meaning that it has more kinds of plants and animals for its size than any other arid area. Of the 5,000 plant species in the region, almost half are restricted to the Succulent Karoo and many of them are succulents – or plant species adapted to store their own water supply in leaves or stems for use in the dry summer. They include vygies (Aizoaceae), daisies (Asteraceae), aloes (Liliaceae), plakkies (Crassulaceae), geraniums (Geraniaceae), melkbos (Euphorbiaceae), kambroo and halfmens (Asclepiadaceae) and others. One third of 10,000 world’s succulent plant species are found here (Cowling and Hilton-Taylor 1999)! There are also some unusual animals: 8/12 kinds of frogs, 30/ 94 reptiles and 20/232 birds are also unique to the Succulent Karoo. The number of insects, spiders and scorpions species in the region is less well known, but many, especially the bees, are special to the region (Vernon 1999). The Nama Karoo with 2,200 plant species is less rich and less unique (450 unique to the region) because many of the plant species are shared with the adjacent Succulent Karoo, grassland and savanna. The significance of the plants and their associated animals to the economy of the Karoo may not be immediately evident to city dwellers, but they are the basis of many Karoo businesses including livestock and game ranching, eco-tourism, science tourism, plant breeding and horticulture, medicinal bioprospecting, as well as having direct non-commercial use value to local users. The valley bottom grazing in Namaqualand is made up of succulents and soft winter-growing annual plants that fatten livestock in winter, Many die in the dry summer as the valleys become hot and dry, storing seeds in the soil for their reappearance in the following winter. The more drought-resistant forage plants are on higher rocky ground, so that large ranches or a nomadic lifestyle are needed for livestock to remain in good condition year round. The spectacular quiver tree and brilliant spring flower carpets are icons of Namaqualand, appearing in artworks, on calendars and screen-savers. Strange dwarf succulents restricted to quarts patches in Namaqualand and the Little Karoo, charismatically called bokkloukies, bababoudjies, gansmis, are popular with succulent collectors and a few small business specialize in their propagation. Some plants have made major contributions horticulture and breeding has resulted in a wealth popular varieties sold worldwide (Sparaxis, Freesia, Lachenalia, Gazania, and the ubiquitous window-box geranium). Plant species, once used by the indigenous people as medicine, are currently being explored as sources of new drugs for treating conditions as diverse as obesity (Hoodia), alcoholism (Sceletium) and cancer (Sutherlandia) (van Wyk et al. 2001). At village level many plants have direct use value. Acacia wood and small dry bushes are collected as fuel for cooking and heating. The traditional “matjieshuise are constructed from mats woven from river reeds. Circular wind shelters (skerms) used for cooking are made by uprooting and stacking common, shallow-rooted succulents to form a thick wall. 3. Agriculture, tourism, mining: opportunities and threats Agriculture, tourism and mining are the basis for business in both the Succulent and Nama Karoo, and have potential to develop the region; but malpractice in any of these sectors will destroy both mainstream business and subsistence economies. In the Namaquland Succulent Karoo tourism and mining compete with and interact with traditional herding. The way the land is managed for livestock productions influences the tourist experience. Over-grazing strips away the vegetation and causes unsightly erosion, but patchy grazing maintains an abundance of annual plants in the rangeland whose flowers paint the landscape with brilliant splashes of colour in spring. Surface mining for diamonds, heavy metals, gypsum and marble destroy the vegetation that supports both livestock and tourism. The law requires that the vegetation be restored, and techniques are now available for putting back all the cover and at least half the plant species that were removed, so that a mined landscape can serve a grazing, and possibly a tourism function once again. If mining companies fail to comply with legislation, the business potential of the region will be permanently “undermined”. Similarly, if either the herders or the “4 by 4” explorers in the Richterveld National Park scar the landscape with their activities, the losers will include subsistence farmers, tourism business and the National Parks. Science and science tourism in the Hantam Karoo faces a similar dilemma but on a smaller scale. Large areas are needed for observatories and telescope arrays, as well as associated accommodation – however, any development needs to consider the local environment and minimise destruction of the special flora of the area. In the Little Karoo, where ostrich farming has been the economic mainstay for two centuries, the negative impact of this industry on ecosystem services is now being felt in other sectors. Grazing has been depleted in valley bottoms, the soil-holding lichen crust stripped away, gullies are forming and soil eroded from the foothills is clogging the rivers and favouring invasions of giant reed, Sesbania and saltbush. Changed farming practices, such as removal of breeding ostrich from natural veld and maintaining them on sown pasture are one of the solutions favoured by the industry. In combination with restoration of damaged veld this solution should generate new opportunities for tourism. Nama Karoo landscapes are spectacular in a bleak and dramatic way. There is plenty of “niks” – wide viewsheds for the crowd-weary traveller and hunter. Opportunities for games farms, guest-farms. Dinosaur bones, engraved stone artefacts, corbled houses and early colonial sheep kraals make this an exciting hunting ground for the science and cultural tourist. However, the early settles also scarred the landscape. The rocky plains are less vulnerable to erosion than the valleys of the succulent Karoo, but the deep alluvial soil along the courses of dry riverbeds were vulnerable. These were the only places that the first European settlers could grow subsistence crops, but damming of these moody rivers, and ploughing of their banks led to silted and broken dams and deep erosion of the silty floodplains. Loss the riparian vegetation and deep soil, and hunting by farm dogs together drove at least one specialised animal, the Riverine rabbit, to extinction (). Restoration of the riparian areas will be needed to protect this species and its habitat. The far more extensive problem is the selective grazing of the vegetation, which on these rocky landscapes has done little to reduce cover, but much to change species composition, converting a once opulent rangeland to one dominated by poisonous and spiny plants. Apart from its grazing resources, the Nama Karoo hides a rich reserve of uranium that accumulated in ancient rivers that may once have flowed from the Richterveld to Rietbron. The mining of this non-renewable capital would lead to short-term mining booms in towns near the ore body and would generate new employment opportunities and skills training. However, risks might include radioactive contamination of ground water and dust, and localised loss of grazing land. Like all mining-related development the benefits are short-lived – perhaps a matter of decades – before the economy must once again rely on sustainable use of renewable natural resources such as grazing land. 4. Ecological and economic role of a sustainability service industry In this section I propose that the business sustainability can be improved by access to specialist services provided by the state and or by private enterprise. Integrated planning is the first step in achieving sustainable development. Integrated planning for rural areas goes beyond the boundaries of urban planning (housing, schools, hospitals) to include such issues as biodiversity corridors (Cowling et al. 1999), traditional transhumance routes, sites of scientific, palaeoecological or cultural significance, solid and liquid waste disposal and recycling, disaster management, subsistence resources (such as woodlots, food gardens) and many other issues. For example, priority areas and corridors for biodiversity conservation need to be identified, demarcated and secured before they are irreversibly transformed by mining or urban development. Town development in the Karoo is water limited and planning for expansions needs to be done with this in mind. Although most Karoo development planning can be done at provincial or municipal level, planning around human population growth and scenarios for providing acceptable education, welfare and health facilities needs to be at national level. Planning of this kind must include strategies for curbing the exponential rate of human population growth whether rural or urban. This is an important issues if quality of life for all is to improve and development in arid Karoo areas is to be truly sustainable. Similarly, exurban development imposes high costs on local municipalities in terms of service provision, and prior zoning rather than ad hoc decisions should determine limits for town sprawl. Integration of the skills of many experts is required to minimise the negative ecological and social impacts of unplanned urban expansion in rural areas. Environmental impact assessment, planning and management interventions in towns, on game ranches, communal land, mines or tourism developments, often require specialised knowledge or skills. Government agricultural and conservation extension services are at present undersupplied in the Karoo. Extension officers advise farmers on numbers and types of livestock, game or crops appropriate for various farming units, inform them about legislation relating to water use, road making and alien vegetation control, advise on erosion control and restoration, and ensure that environmental and agricultural resources legislation was understood and complied with. Although these roles are partly served by LandCare, Agriculture, Cape Nature and other government agencies such as DWAF Working for Water and Working for Woodlands programmes, private enterprise has is now supplying many sustainability services in rural areas. Well informed and ethical environmental consultants can potentially make major contributions to ameliorating the negative impacts of development. The past ten years has seen the growth of other sustainability service businesses such as erosion control, alien vegetation clearing, indigenous seed production and veld restoration, waste water treatment, composting, recycling, indigenous landscaping, and a growth in the demand for books on these topics (Coetzee 2005; Esler et al 2006). Many opportunities exist for the development for example of energy-efficient homes, solar alternatives to use of wood and electricity, composting toilets – all technologies that will contribute to making development of towns in arid area more sustainable. The sustainability service sector has great potential for providing employment and offers opportunities for micro-enterprise development. Examples of the potential for this business model are the newly trained ecological restoration crews now operating independently on sand mines on the Namaqualand coast (Van Eeden et al. 2007; Carrick and Kruger 2007). However, to ensure rapid growth of sustainability service micro-enterprises, it is essential that Karoo towns ensure that children receive basic welfare, health services and education. Safety, security, social welfare, and human resource development are all an essential part of ensuring that Karoo business in ecologically and economically sustainable. In brief, the Karoo is has potential for agriculture, tourism, mining, but development has water and biodiversity costs. Destruction of Karoo Natural Capital will kill business, and reduce future options, leaving damaged landscapes and destitute people. Social and environmental sustainability services Aronson, J, Milton, S.J. and Blignaut, J. N. (eds) 2007. Restoring natural capital : science, business, and practice. Island Press, Covalo, USA Beinart, W. 2003. The rise of conservation in South Africa – settlers, livestock and the environment 1770-1950. Oxford University Press. Carrick, P.J. and Kruger, R. 2007. Restoring degraded landscapes in lowland Namaqualand: Lessons from the mining experience and from regional ecological dynamics. Journal of Arid Environments 70:767-781 Coetzee, K. 2005. Caring for natural Rangelands. University of KwaZulu-Natal Press. (order from books@ukzn.ac.za) Cowling , R.M. and Hilton-Taylor, C. 1999. Plant biogeography, endemism and diversity. Pp 42-56 in: Dean, W.R.J. and Milton, S.J. (eds). The Karoo, ecological patterns and processes. Cambridge University Press. Cowling, R.M., Pressey, R.L., Lombard, A.T., Desmet, P.G. and Ellis, A.G. 1999. From
representation to persistence: requirements for a sustainable system of conservation areas
in the species-rich mediterranean-climate desert of southern Africa. Diversity and
Distributions
5:51-71
Deacon, H.J. & Deacon, J. 2003. Human Beginnings in South Africa. David Philip, Claremont. Dean, W. R. J. and Macdonald, I. A. W. 1994. Historical changes in stocking rates of
domestic livestock as a measure of semi-arid and arid rangeland degradation in the Cape
Province, South Africa. Journal of Arid Environments 26:281-298.
Esler, K.J., Milton, S.J. & Dean, W.R.J. 2006. Karoo Veld - Ecology and Management. Briza Press, Pretoria. 224 pages. ISBN 1 875093 52 4 (English), ISBN 1 875093 55 9 (Afrikaans) Hoffman, M.T. and Ashwell, A. 2001. Land degradation in South Africa. University of Cape Town Press Nel, E. and Hill, T. 2008. Marginalisation and demographic change in the semi-arid Karoo, South Africa Journal of Arid Environments 72: 2264-227. Penn, N. G. 1987. The frontier in the Western Cape, 1700-1740. In Papers in the Prehistory
of the Western Cape, South Africa
, ed. J. Parkington and M. Hall, pp. 462-503. Oxford: BAR
International Series, 332
Shaw, J. 1875. On the changes going on in the vegetation of S.A. through the introduction of
the Merino sheep. Journal of the Linnean Society 14, 202-208.Smith, A.B. 1999. Hunters and
herders in the karoo landscape. Pp 243-246 in: Dean, W.R.J. and Milton, S.J. (eds). The
Karoo, ecological patterns and processes
. Cambridge University Press.
Talbot, W. J. 1961. Land utilization in the arid regions of southern Africa. Part I. South Africa. In A history of land use in arid regions. Arid Zones Research, 17, ed. L. D. Stamp, pp. 299-338. Paris: UNESCO van Eeden, J.D., Lubke, R.A. and Haarhoff, P. 2007. Return of Natural, Social, and Financial Capital to the Hole Left by Mining. Pages 198-208 in Aronson, J, Milton, S.J. and Blignaut, J. N. Restoring natural capital : science, business, and practice. Island Press, Covalo, USA. van Wyk, BE et al 2001. Peoples plants. Briza Press. Vernon, C.J. 1999. Biogeography, endemism and diversity of animals in the karoo. Pp 57-78 in: Dean, W.R.J. and Milton, S.J. (eds). The Karoo, ecological patterns and processes. Cambridge University Press.

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