Comparação de técnicas no diagnóstico da infecção leptospírica em ovinos e implicações na saúde pública

Fundação de Amparo à Pesquisa do Estado de São Paulo (FAPESP)

Fatores de risco e prevalência de animais domésticos e silvestres portadores de anticorpos contra Vaccinia Vírus na região centro oeste do Estado de São Paulo

Conselho Nacional de Desenvolvimento Científico e Tecnológico (CNPq)

Necessidade de vigilância epidemiológica para Leishmania infantum (syn. Leishmania chagasi) e Leishmania (Viannia) braziliensis em flebotomíneos e gatos errantes no Bosque Municipal de Marília-SP

Pós-graduação em Medicina Veterinária - FMVZ

An assessment of the economic impact of climate change on the water sector in the Turks and Caicos Islands

The best description of water resources for Grand Turk was offered by Pérez Monteagudo (2000) who suggested that rain water was insufficient to ensure a regular water supply although water catchment was being practised and water catchment possibilities had been analysed. Limestone islands, mostly flat and low lying, have few possibilities for large scale surface storage, and groundwater lenses exist in very delicate equilibrium with saline seawater, and are highly likely to collapse due to sea level rise, improper extraction, drought, tidal waves or other extreme event. A study on the impact of climate change on water resources in the Turks and Caicos Islands is a challenging task, due to the fact that the territory of the Islands covers different environmental resources and conditions, and accurate data are lacking. The present report is based on collected data wherever possible, including grey data from several sources such as the Intergovernmental Panel on Climate Change (IPCC) and Cuban meteorological service data sets. Other data were also used, including the author’s own estimates and modelling results. Although challenging, this was perhaps the best approach towards analysing the situation. Furthermore, IPCC A2 and B2 scenarios were used in the present study in an effort to reduce uncertainty. The main conclusion from the scenario approach is that the trend observed in precipitation during the period 1961 - 1990 is decreasing. Similar behaviour was observed in the Caribbean region. This trend is associated with meteorological causes, particularly with the influence of the North Atlantic Anticyclone. The annual decrease in precipitation is estimated to be between 30-40% with uncertain impacts on marine resources. After an assessment of fresh water resources in Turks and Caicos Islands, the next step was to estimate residential water demand based on a high fertility rate scenario for the Islands (one selected from four scenarios and compared to countries having similar characteristics). The selected scenario presents higher projections on consumption growth, enabling better preparation for growing water demand. Water demand by tourists (stopover and excursionists, mainly cruise passengers) was also obtained, based on international daily consumption estimates. Tourism demand forecasts for Turks and Caicos Islands encompass the forty years between 2011 and 2050 and were obtained by means of an Artificial Neural Networks approach. for the A2 and B2 scenarios, resulting in the relation BAU>B2>A2 in terms of tourist arrivals and water demand levels from tourism. Adaptation options and policies were analysed. Resolving the issue of the best technology to be used for Turks and Caicos Islands is not directly related to climate change. Total estimated water storage capacity is about 1, 270, 800 m3/ year with 80% capacity load for three plants. However, almost 11 desalination plants have been detected on Turks and Caicos Islands. Without more data, it is not possible to estimate long term investment to match possible water demand and more complex adaptation options. One climate change adaptation option would be the construction of elevated (30 metres or higher) storm resistant water reservoirs. The unit cost of the storage capacity is the sum of capital costs and operational and maintenance costs. Electricity costs to pump water are optional as water should, and could, be stored for several months. The costs arising for water storage are in the range of US$ 0.22 cents/m3 without electricity costs. Pérez Monteagudo (2000) estimated water prices at around US$ 2.64/m3 in stand points, US$ 7.92 /m3 for government offices, and US$ 13.2 /m3for cistern truck vehicles. These data need to be updated. As Turks and Caicos Islands continues to depend on tourism and Reverse Osmosis (RO) for obtaining fresh water, an unavoidable condition to maintaining and increasing gross domestic product(GDP) and population welfare, dependence on fossil fuels and vulnerability to increasingly volatile prices will constitute an important restriction. In this sense, mitigation supposes a synergy with adaptation. Energy demand and emissions of carbon dioxide (CO2) were also estimated using an emissions factor of 2. 6 tCO2/ tonne of oil equivalent (toe). Assuming a population of 33,000 inhabitants, primary energy demand was estimated for Turks and Caicos Islands at 110,000 toe with electricity demand of around 110 GWh. The business as usual (BAU), as well as the mitigation scenarios were estimated. The BAU scenario suggests that energy use should be supported by imported fossil fuels with important improvements in energy efficiency. The mitigation scenario explores the use of photovoltaic and concentrating solar power, and wind energy. As this is a preliminary study, the local potential and locations need to be identified to provide more relevant estimates. Macroeconomic assumptions are the same for both scenarios. By 2050, Turks and Caicos Islands could demand 60 m toe less than for the BAU scenario.

As assembléias de peixes da represa de Jurumirim (alto rio Paranapanema, SP): status atual e mudanças históricas

Coordenação de Aperfeiçoamento de Pessoal de Nível Superior (CAPES)

Efeitos da tilapicultura em tanques-rede sobre as assembléias zooplanctônicas do Reservatório de Chavantes, rio Paranapanema (SP/PR)

Conselho Nacional de Desenvolvimento Científico e Tecnológico (CNPq)

A ictiofauna agregada a um sistema de piscicultura em tanques-rede na represa oligotrófica de Chavantes (médio rio Paranapanema, SP/PR): composição de espécies e atributos ecológicos

Coordenação de Aperfeiçoamento de Pessoal de Nível Superior (CAPES)

Impacto das arraias (Myliobatiformes: Potamotrygonidae) na população ribeirinha e demais frequentadores do alto curso do Rio Paraná e alguns afluentes

Coordenação de Aperfeiçoamento de Pessoal de Nível Superior (CAPES)

Aspectos da biologia populacional de Pimelodus maculatus (Teleostei: Siluformes), sob a influência de sitemas de piscicultura em tanques-rede

Conselho Nacional de Desenvolvimento Científico e Tecnológico (CNPq)

Caracterização do regime alimentar de Oreochromis niloticus (Linnaeus, 1758) e Tilapia rendalli (Boulenger, 1897) na represa de Barra Bonita, Médio Rio Tietê, SP

Coordenação de Aperfeiçoamento de Pessoal de Nível Superior (CAPES)

Efeitos dos pulsos de vazão dos reservatórios do baixo rio Paranapanema (SP/PR) sobre os sistemas de jusante - variáveis físicas, químicas e assembléias zooplanctônicas (Cladocera e Copepoda)

Fundação de Amparo à Pesquisa do Estado de São Paulo (FAPESP)

Abordagens multivariadas no estudo da dinâmica de comunidades de macrófitas aquáticas

Conselho Nacional de Desenvolvimento Científico e Tecnológico (CNPq)

Efeito de pontas de pulverização e de arranjos populacionais de plantas de Eichhornia crassipes (Mart.) Solms., Salvinia auriculata Aubl. e Pistia stratiotes L. na deposição de calda de pulverização

Coordenação de Aperfeiçoamento de Pessoal de Nível Superior (CAPES)

Características limnológicas em áreas sob influência de piscicultura em tanques-rede no reservatório da UHE Chavantes, rio Paranapanema, SE/S, Brasil

Coordenação de Aperfeiçoamento de Pessoal de Nível Superior (CAPES)

Espacialização do biovolume de plantas aquáticas submersas a partir da integração de dados obtidos por sensores remotos

Coordenação de Aperfeiçoamento de Pessoal de Nível Superior (CAPES)