A Comparison of the Management Models of Protected Areas between China and the Southern African Region

A Comparison of the Management Models of Protected Areas between China and the African South Region allows reading and evaluating the similarities and differences in the use of management model as a management tool for protected areas in China and South African Region. Specifically, some positive and negative features of the management approaches for the two regions. Secondary data was collected from various related literature such as policy documents, students‟ dissertations/thesis, scientific articles and magazines. Based on the method above, the study found out that China's first nature reserve was the Dingus Mountain Nature Reserve in Zhaoqing, Guangdong province established in 1956. By the end of 2005, about 2,349 nature reserves of various kinds were set up throughout the country, covering a total area of 149.95 million ha and accounting for 15 percent of the total land territory. The study further found that Southern Africa has approximately 4,390 protected areas out of 11487920 total land areas and Eastern Africa has approximately 1838144 protected areas, which is equivalent to 15.0% of the total land areas. South Africa in this region had its first declared natural park in 1926 after Paul Kruger (a war hero) had alerted the authorities of the extinguishing threat of some animal species of region.

Assessement of Malaria Transmission in an Area with Very Low Mosquito Density

The increase in world travel in recent years, especially to and from areas where vector-borne diseases are endemic, has resulted in a substantial rise in imported cases of those diseases. In particular, malaria is a cause of concern. In those countries at the edge of its distribution, it can be difficult to distinguish between autochthonous and imported cases. However, distinguishing between the two is important because of the different allocation of resources to combat the disease that each requires. In general, observation of the various stages of parasite development in wild-caught female mosquitoes is considered evidence of autochthonous transmission. Observation of oocysts in the mosquito mid-gut testifies that mosquitoes are susceptible to infection but conclusions cannot be reached about their ability to complete the transmission cycle. Perhaps the best indication of autochthonous transmission is microscopic observation of sporozoites in mosquito salivary glands, since this detects parasites ready to be inoculated (BELER et al., 1990). Detection of circumsporozoite protein (CSP)(BURKOT, WILLIAMS & SCHNEIDER, 1984) in dry mosquito thoraxes, by Enzyme Linked Immunosorbent Assay (ELISA) is also widely used to determine transmission, especially when large numbers of mosquitoes need to be processed. Such assays provide information about the parasite species infecting the mosquito (BURKOT & WIRTZ, 1986; WIRTZ et al., 1987; BELER et al., 1990).

Assessment and mapping the sensitive areas to desertification in an insular Sahelian mountain region Case study of the Ribeira Seca Watershed, Santiago Island - Cabo Verde

This paper presents the assessment and mapping of the Ribeira Seca catchment, an insular Sahelian mountain region sensitive to desertification, located on the island of Santiago, Cabo Verde. Desertification is a threat to the global environment, representing a serious ecological problemin Cabo Verde. To successfully combat desertification, an evaluation of desertification consequences is required and the building of cartography of the sensitivity for arid and semi-arid ecosystems is required as a first step. The MEDALUS model was the basis for this study in which six quality indicators were used: climate, soil, vegetation, land management, erosion and social factors. Several parameters were defined for each indicator with weights varying between 1 (very low) and 2 (very high). The geometric mean of each of the six quality indicators was employed to produce a map of areas sensitive to desertification. The results of this study show that more than 50% of the watershed show clear evidence of becoming a desertified area.

IDENTIFICAÇAO DE AREAS APTAS À IMPLEMENTAÇAO DE ATERROS SANITARIOS NA ILHA DE SANTIAGO

Pretende-se, com o presente estudo para dissertação, enquadrado como pré-requisitos para obtenção do grau de mestrado no curso de Ordenamento e Desenho do Território, apresentar uma proposta destinada à identificação de areeas destinadas à implementação de um aterro sanitário na ilha de Santiago. Este estudo assenta na utilização de vários parâmetros que nos permitiria ter uma localização georreferenciada para o aterro sanitário que serviria os 9 municípios da ilha de Santiago – Cabo Verde. A primeira tarefa terá como ponto de partida a estrutura de um banco de dados que permita avaliar os factores intervenientes no processo de avaliação do problema como a geologia, topografia, mapa viário, vegetação, … A ilha de Santiago, constituído por 9 municípios, não possui uma única estação de tratamento final dos resíduos sólidos urbano (RSU), que diariamente são colectados e que tem como destino final os diferentes locais, a céu aberto, sem mínimo de tratamento. Com a construção do aterro sanitário, permite a recolha de dados, no que se refere a quantidade depositada, assim como os diferentes tipos de materiais, que poderá levar a reciclagem dos diferentes componentes, reduzindo, consideravelmente, os impactos ambientais gerados por estas actividades, bem como os custos decorrentes. Este trabalho teve como objetivo a utilização do Sistema de Informação Geográfica (SIG) na identificação de áreas potenciais para a instalação de aterros sanitários que sirva toda a ilha de Santiago. Foram consideradas as características físicas, sócio-econômicas da ilha e normas técnicas existentes. Os procedimentos empregados envolveram a edição e manipulação de dados cartográficos e temáticos, a definição de parâmetros de restrição e sobreposição topológica, desenvolvidos no âmbito de um Sistema de Informação Geográfica. No final, foram identificadas áreas potenciais para instalação de aterros sanitários. Esta é uma demonstração prática de que os SIG's podem ser empregados para a solução de problemas ambientais