scholarly journals O PROCESSO DE ESTUDO E IMPLANTAÇÃO DE PCHS E A IMPORTÂNCIA DO LICENCIAMENTO AMBIENTAL PARA A COMUNICAÇÃO ENTRE EMPREENDEDORES E COMUNIDADE LOCAL

2019 ◽  
Vol 34 (01) ◽  
pp. 94-104
Author(s):  
Mariana Wagner de Toledo Piza ◽  
Osmar De Carvalho Bueno ◽  
Francisco José Blasi de Toledo Piza

O PROCESSO DE ESTUDO E IMPLANTAÇÃO DE PCHS E A IMPORTÂNCIA DO LICENCIAMENTO AMBIENTAL PARA A COMUNICAÇÃO ENTRE EMPREENDEDORES E COMUNIDADE LOCAL   MARIANA WAGNER DE TOLEDO PIZA1; OSMAR DE CARVALHO BUENO2; FRANCISCO JOSÉ BLASI DE TOLEDO PIZA3   1Economia, Sociologia e Tecnologia, Universidade Estadual Paulista (Unesp), Faculdade de Ciências Agronômicas, Botucatu, R. José Barbosa de Barros, 1780, JardimParaíso, CEP: 18610-034, Botucatu, São Paulo, Brasil, [email protected] 2Economia, Sociologia e Tecnologia, Universidade Estadual Paulista, Universidade Estadual Paulista (Unesp), Faculdade de Ciências Agronômicas, Botucatu, R. José Barbosa de Barros, 1780, JardimParaíso, CEP: 18610-034, Botucatu, São Paulo, Brasil, [email protected] 3Engenharia de Produção, Faculdade Iteana de Botucatu, Av. Alcides Cagliari, 2601, Jardim Aeroporto, CEP: 18606-855, Botucatu, São Paulo, Brasil, [email protected]   RESUMO: O trabalho objetivou apresentar o processo de estudo para implantação de Pequenas Centrais Hidrelétricas (PCHs), o momento em que a comunidade local participa deste processo e a importância de sua efetiva participação. Utilizou-se a realidade brasileira no que tange o estudo para implantação de PCHs, a legislação nacional e órgãos envolvidos no processo como: Agência Nacional de Energia Elétrica (ANEEL), Agência Nacional de Águas (ANA), Departamento de Água e Energia Elétrica (DAEE) e Companhia Ambiental do Estado de São Paulo (CETESB). O processo de estudo de um potencial hidráulico conta com cinco fases: Estimativa do Potencial Hidrelétrico; Inventário Hidrelétrico; Estudo de Viabilidade; Projeto Básico e Projeto Executivo. Em consonância a este processo é necessário realizar o Estudo de Impacto Ambiental (EIA) e o respectivo Relatório de Impacto Ambiental (Rima). Como ambiente de diálogo entre todos os atores envolvidos, o processo de licenciamento ambiental conta com as audiências públicas, nessas devem ocorrer trocas de informações e conhecimento das demandas dos diversos envolvidos, inclusive da comunidade local, sua efetiva participação é fundamental para a otimização o projeto nos âmbito socioambiental.   Palavras-chaves: PCHs, licenciamento ambiental, comunicação.   THE SHPs STUDY AND IMPLEMENTATION PROCESS AND IMPORTANCE OF ENVIRONMENTAL LICENSING FOR COMMUNICATION BETWEEN ENTREPRENEURS AND LOCAL COMMUNITY   ABSTRACT: The aim of this paper was to present the process of study and implementation of Small Hydroelectric Power Plants (SHPs), local community participation and the importance of their effective participation. The Brazilian reality was used in the study for the implementation of SHPs, as well as, national legislation and public agencies involved in the process, such as: National Electricity Agency (ANEEL), National Water Agency (ANA), Department of Water and Electric Energy (DAEE) and Environmental Company of the State of São Paulo (CETESB). The process of hydraulic potential study has five stages: hydropower potential estimation; hydraulic inventory; viability study; basic project and executive project.  It is also necessary to carry out the Environmental Impact Study (EIA) and Environmental Impact Report (RIMA). According to all the actors involved, the environmental licensing process relies on public hearings, where must occur change of information and knowledge stakeholders demands, including the local community, which effective participation is fundamental for the optimization of the project socio-environmental scope. Keywords: SHPs, environmental licensing, communication.

2020 ◽  
Vol 11 (6) ◽  
pp. 1952
Author(s):  
Raiane Real Martinelli ◽  
Gessuir Pigatto ◽  
Timoteo Ramos Queiroz ◽  
Ferenc Istvan Bánkuti

Aquaculture is one of the fastest-growing food sectors in Brazil. Cage fish farming has been widely practiced in the country, mainly in hydroelectric reservoirs. However, different regulatory, technical, and economic challenges may need to be overcome before the sector can achieve increased national and international competitiveness. This study aimed to analyze and compare the competitiveness of tilapia cage farms located on different sides of the Canoas I hydroelectric reservoir, which forms the border between the states of São Paulo and Paraná, Brazil. Structured questionnaires were administered to all fish farmers in the reservoir. Questions about seven competitiveness indicators were rated on a 5-point Likert scale. The results revealed that the major barriers to competitiveness are the institutional environment and environmental sustainability. Paraná has an active environmental inspection service, but São Paulo does not. As a result, tilapia fish farmers in Paraná gave more importance to environmental compliance than those located in São Paulo.


2010 ◽  
Vol 43 (5) ◽  
pp. 516-522 ◽  
Author(s):  
Almério de Castro Gomes ◽  
Marcia Bicudo de Paula ◽  
Delsio Natal ◽  
Sabina Léa Davidson Gotlieb ◽  
Luis Filipe Mucci

INTRODUCTION: Study of the temporal activity of malaria vectors during the implantation of a hydroelectric power station on the River Paraná, intended to generate electrical energy. The river separates the States of São Paulo and Mato Grosso do Sul, in Brazil. The objective was to verify whether alterations occurred in the wealth and diversity indices of Anopheles, following two successive floods, extended to the temporal activity and nycthemeral rhythm followed over a five year period. METHODS: Mosquito capture was performed monthly using the Human Attraction Technique and Shannon Traps. The first, executed for 24h, provided the nycthemeral rhythm and the second, lasting 15h, permitted the tracking of Anopheles during the two floods. RESULTS: The bimodal pattern of Anopheles darlingi defined before these floods was modified throughout the environment interventions. The same effect had repercussions on the populations of An albitarsis s.l., An triannulatus and An galvaoi. Activity prior to twilight was less affected by the environment alterations. CONCLUSIONS: The dam construction provoked changes in Anopheles temporal activity patterns, permitting classification of the area as an ecologically steady and unstable situation. Differences observed in Anopheles behavior due to the capture methods revealed the influence of solo and multiple attractiveness inside the populations studied.


2021 ◽  
Vol 2 (2) ◽  
pp. 146-154
Author(s):  
Zoltán Korényi

Összefoglaló. A dolgozat témája a különböző erőműfajták életciklusra vonatkozó fajlagos anyagigényének a vizsgálata. Az elemzések a nemzetközi szakirodalmi források felhasználásával történtek. Módszere, a bázisadatok elemzése, majd az anyagigényeknek az erőmű beépített teljesítményére és az életciklus alatt megtermelt villamosenergiára vonatkoztatott fajlagos értékek meghatározása. Az eredmények azt mutatják, hogy a nap- és szélerőművek elterjedésével a hagyományos erőművek által felhasznált fosszilis energiaforrások (pl. a szén) bent maradnak ugyan a földben, de cserébe az új technológia legyártásához a hagyományos anyagokból (beton, acél, alumínium, réz stb.) fajlagosan jóval nagyobb mennyiségekre lesz szükség. Emellett megnő a ritkán előforduló fémek (gallium, indium stb.) felhasználása, ami Európában, a lelőhelyek hiányában, új kockázatokkal jár. Summary. The topic of the study is to determine the material use of different power plant types. This is a part of the known life cycle analysis (LCA). The aim of LCA is to determine the impact of human activity on nature. The procedure is described in the standards (ISO 14040/41/42/42). Under environmental impact we mean changes in our natural environment, air, water, soil pollution, noise and impacts on human health. In the LCA, the environmental impact begins with the opening of the mine, continues with the extraction and processing of raw materials, and then with the production of equipment, construction and installation of the power plant. This is followed by the commissioning and then operation of the power plants for 20-60 years, including maintenance. The cycle ends with demolition, which is followed by recycling of materials. The remaining waste is disposed of. This is the complex content of life cycle analysis. Its purpose is to determine the ecological footprint of man. The method of the present study is to isolate a limited area from the complex LCA process. This means determining the amount of material needed to build different power plants, excluding mining and processing of raw materials. Commercially available basic materials are built into the power plant’s components. The research is based on the literature available in the international area. The author studied these sources, analysed the data, and checked the authenticity. It was not easy because the sources from different times, for different power plants showed a lot of uncertainty. In overcoming the uncertainties, it was a help that the author has decades of experience in the realisation of power plants. It was considered the material consumption related to the installed electricity capacity of the power plant (tons/MW) as basic data. The author then determined the specific material consumptions, allocated to the electric energy generated during the lifetime, in different power plants. The calculation is carried out with the help of the usual annual peak load duration hours and the usual lifetime of the power plants. The results show that with the spread of solar and wind energy, the fossil energy sources previously needed for conventional power plants will remain inside the Earth, but in exchange for the production of new technological equipment from traditional structural materials (concrete, steel, aluminium, copper and plastic), the special need multiplies. If we compare the power plants using renewable energy with the electric energy produced during the life cycle of a nuclear power plant, the specific installed material requirement of a river hydropower plant is 37 times, that of an onshore wind farm it is 9.6 times, and that of an outdoor solar power park is 6.6 times higher. Another important difference is that wind turbines, solar panels and batteries also require rare materials that do not occur in Europe (e.g. gallium, indium, yttrium, neodymium, cobalt, etc.). This can lead to security risks in Europe in the long run.


2021 ◽  
Vol 24 ◽  
Author(s):  
Silvia Sayuri Mandai ◽  
Raphaela Martins de Carvalho ◽  
Marcelo Marini Pereira de Souza

Abstract The state of São Paulo has a history of habitat loss and fragmentation in endemic areas with projects that threaten its biodiversity. Therefore, this study analyzed how the Environmental Impact Statements (EISs) of mining activities of the state of São Paulo (2005-2016) considered the biodiversity theme in different chapters. To analyze the ten selected EISs, we used the Index of Biodiversity Inclusion (IBI), which reflects the analysis of environmental indicators (from 0 to 1), depending on the commitment presented in each of the indicators. The IBI values ranged from 0.25 to 0.67 with significant variation among EISs. Most of them partially met the criteria, which was a profile similar to other countries, representing information gaps in most of the chapters covering biodiversity. The shortcomings were data limitation, impact analysis, and inadequate mitigation measures, in which the study highlights the need for a better scoping definition previous to Environmental Impact Assessment.


2018 ◽  
Vol 33 (1) ◽  
pp. 153-163 ◽  
Author(s):  
Luísa Carolina Silva Lelis ◽  
Raoni Wainer Duarte Bosquilia ◽  
Sergio Nascimento Duarte

Abstract This study aimed to verify the performance of the information produced by the GPM (Global Precipitation Measurement) mission and TRMM (Tropical Rainfall Measurement Mission) on the eastern region of São Paulo state, based on a comparison of rainfall data from DAEE (Department of Waters and Electric Energy of São Paulo State). The comparison was done by comparing spatially aggregated information from both sources. In order to analyze the results, we measured: (1) Relative Difference, (2) BIAS and (3) Root Mean Square Error (RMSE). It was found that the relative differences were in the range of -20% to 20% for both missions. Analyzing the BIAS for both satellites it was observed that 68% of the measurements were overestimated. The highest agreement was obtained for the mesoregion of Campinas and the lowest for Araraquara. In the TRMM, the lowest RMSE values were found in the Araraquara mesoregion and the highest in Piracicaba. In the GPM the closest measured values were observed in the Piracicaba mesoregion, while the most distant values were identified in Araraquara. All the analyzes of this work demonstrated similarity between the errors generated by both satellites. New comparison studies are needed to better understand the products.


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