995 resultados para VEGETATION HISTORY


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A benthic survey was carried out from November 1998 to December 1999 in the tidal flats of Bahía Samborombón (Río de la Plata estuary, Argentina), in order to study the population structure, reproductive aspects, growth and secondary production of Capitella capitata (Fabricius, 1780). Growth was analyzed using ELEFAN routine, and the secondary production was estimated by Hynes and Coleman's method (1968). C. capitata did not present periods of very important recruitments throughout the year; however, the abundance of smallest size classes was higher during summer and autumn. The summer cohort showed a growth rate (K) of 2.05 and a seasonal growth oscillation (C) of 0.6, pointing out that worms grew very slowly during winter months. The life span of this cohort was 13 months. The autumn cohort showed a lower growth rate (K= 1.5) and its growth was lowest during winter. The life span was 15 months for this cohort. C. capitata in Punta Rasa presented an extended reproductive period, with absence of activity during winter months. The type of eggs and larvae suggest that C. capitata has benthic larval development in the study area, destining its reproductive effort to the production of a low number of eggs, and assuring larvae survival through incubation in brooding tubes. The annual mean biomass in Punta Rasa was 0.117 g m-2 (AFDW), with a mean secondary production of 0.23 g m-2 y-1 and a P/B ratio of 1.96 y-1. The relatively low density, biomass production and P/B ratio of C. capitata in Punta Rasa can be considered as reference values for this species inhabiting undisturbed or moderately disturbed areas.

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Ao longo de quase cinco anos de trabalho, foi desenvolvido o Índice de Qualidade dos Municípios - Verde, pela Fundação CIDE. O trabalho buscou retratar as características da fragmentação florestal fluminense. Como um elemento para apoiar a gestão ambiental do território, o projeto identificou corredores ecológicos prioritários para a interligação de fragmentos florestais. A grande contribuição do trabalho, do ponto de vista conceitual, foi reorientar o debate acerca da fragmentação florestal no Estado do Rio de Janeiro. O projeto IQM - Verde apresentou, exaustivamente, lugares onde ocorreram perdas e ganhos de estoques de vegetação com porte arbóreo, num recorte por municípios, bacias hidrográficas e Unidades de Conservação. Existem importantes questões que foram levantadas e ainda aguardam maiores e melhores respostas. Uma delas é tentar explicar, a partir da ecologia de paisagens, quais são os mecanismos que facilitam ou dificultam o processo natural de sucessão florestal. A situação da sucessão florestal é completamente diferente de uma região para outra do Estado. No Noroeste do Estado existem indícios claros de retração e fragmentação dos remanescentes enquanto na região Serrana do Sul Fluminense aparecem sinais claros de recuperação e recomposição florestal. Novos conceitos de gestão ambiental procuram minimizar os efeitos decorrentes da fragmentação e do isolamento espacial das espécies. O aumento da conectividade através de corredores ecológicos entre unidades de conservação e até mesmo entre os fragmentos mais bem conservados é apontado por muitos pesquisadores como uma das formas mais eficazes de promover a manutenção dos remanescentes florestais - a longo prazo - e até mesmo promover a recuperação funcional de determinadas unidades ecológicas atualmente ilhadas. A atual geração de pesquisadores e gestores públicos está diante do problema do controle dos processos que desencadeiam a fragmentação florestal. Portanto, é urgente a necessidade de entender todas as consequências associadas ao processo de fragmentação florestal e, ao mesmo tempo, descobrir os efeitos inibidores deste complexo fenômeno que possui raízes físicas, naturais e sociais. O objetivo central da tese é, a partir de elementos da História das Mentalidades e da Teoria da Decisão, construir cenários de pressão antrópica sobre os remanescentes florestais e propor um programa possível de intervenção econômica, jurídica e política, denominado no presente estudo como bolsa floresta, capaz de aliviar o atual processo de fragmentação florestal.

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This is the history of contamination in sediments from the Mersey Estuary: Development of a chronology for the contamination of the Mersey Estuary by heavy metals and organochlorines Report produced by the Environment Agency in 1998. This report looks at the history of industrial contamination of the Mersey and Ribble Estuaries back to the early part of the last century, many decades before the start of monitoring programmes providing a remarkably detailed picture of very complex changes. There is a clear record in the sediment of the contamination by each heavy metal (including: Cu, Cr, Hg, Pb, Zn) and organochlorine chemical (including DDT isomers and PCB congeners) studied. The results of the study clearly show the increases in levels of contamination as industry expanded early last century followed by various improvements as this century progressed. Each pollutant has its own idiosyncratic pattern of change with some improvements predating modern environmental concerns whilst other changes seem to relate directly to recent improvements in legislative control. Overall, for the pollutants studied, the results clearly demonstrate the magnitude of improvement that has been achieved in what was a very polluted area. The only major reservation to this story is that despite the wide range of substances covered, many other potentially important pollutants remain to be studied in a similar manner.

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This is the Mersey Estuary Saltmarsh vegetation survey 2002 report produced by the English Nature Cheshire in 2003. This report looks at the mapping of vegetation communities on the saltmarsh of the Mersey Estuary. The total area of saltmarsh and associated communities within the Mersey Estuary was found to be 724.1 ha. Most of the saltmarsh in the Mersey Estuary is presently ungrazed or only very lightly grazed, creating a very rank sward in excess of 20 cm in height which is not generally suitable for grazing or roosting birds. On the northern side of the Mersey Estuary, the saltmarsh around the Hale Decoy was lightly grazed by horses, but the remainder was ungrazed. On the south side, the saltmarsh was fairly heavily sheep-grazed along the Frodsham Score, very lightly grazed at Ince Banks by sheep straying from Frodsham and ungrazed at Stanlow Banks. Despite much of it presently being ungrazed, the saltmarsh of the Mersey Estuary is relatively poor in plant species. It appears that this is because the ungrazed areas have been so for less than 20 years and have thus not had time to develop the diversity of a long-established ungrazed marsh. However, withdrawal or depletion of grazing has produced a rank sward which is less valuable to grazing and roosting birds.

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