954 resultados para Ecological Sustainability


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Environmental variability affects the distributions of most marine fish species. In this analysis, assemblages of rockfish (Sebastes spp.) species were defined on the basis of similarities in their distributions along environmental gradients. Data from 14 bottom trawl surveys of the Gulf of Alaska and Aleutian Islands (n=6767) were used. Five distinct assemblages of rockfish were defined by geographical position, depth, and temperature. The 180-m and 275-m depth contours were major divisions between assemblages inhabiting the shelf, shelf break, and lower continental slope. Another noticeable division was between species centered in southeastern Alaska and those found in the northern Gulf of Alaska and Aleutian Islands. The use of environmental variables to define the species composition of assemblages is different from the use of traditional methods based on clustering and nonparametric statistics and as such, environmentally based analyses should result in predictable assemblages of species that are useful for ecosystem-based management.

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Esta pesquisa tem por objetivo analisar os conflitos socioambientais envolvendo os pescadores artesanais na Baía de Ilha Grande e as iniciativas institucionais que buscam dar tratamento a esses conflitos de forma compartilhada. Neste sentido, foram consideradas duas iniciativas institucionais: i) o Projeto Desenvolvimento e Gerenciamento dos Sistemas de Gestão da Pesca e Aquicultura na baía de Ilha Grande GPESCA-BIG; e ii) o Termo de Compromisso entre a Estação Ecológica de Tamoios e as comunidades pesqueiras de Angra dos Reis e Paraty. A metodologia envolveu a observação direta da autora em reuniões de conselhos consultivos e grupos de trabalho em unidades de conservação, em especial, os espaços envolvendo a Estação Ecológica de Tamoios, além de apresentações e audiências públicas sobre a proposta de Acordos de Pesca. Utilizou-se também a observação participante em reuniões e oficinas no âmbito do projeto GPESCA-BIG. De forma complementar, a pesquisa se baseou em entrevistas (formais e informais) e análise de documentos diversos elaborados por entidades representativas dos pescadores e demais atores direta e indiretamente envolvidos no conflito. Foram identificadas três grandes grupos de conflitos relacionados aos pescadores artesanais: (1) sobreposição de territórios de pesca/pesqueiros e as áreas protegidas, principalmente aqueles relacionados à ESEC Tamoios; (2) conflitos associados à pesca industrial, identificados pelos pescadores como barcos de fora, e em menor escala, as embarcações de petróleo/gás e do turismo e; (3) conflitos resultantes da falta de regularização/permissionamento da atividade. Em síntese, estes conflitos envolvem políticas de desenvolvimento e de conservação, que se confrontam com o modo de vida tradicional dos pescadores artesanais e caiçaras. Além dos conflitos oriundos das diferentes formas de apropriação do espaço marinho, estes conflitos também estiveram relacionados ao papel paradoxal do Estado no estabelecimento das regras e normas de ordenamento (incluindo-se a fiscalização/monitoramento ambiental), à burocracia e às diversas instituições existentes para tratar de problemas comuns, tornado confuso o gerenciamento da atividade. No que se refere às iniciativas em análise, os resultados demonstram a existência de instituições relativamente bem constituídas na região, com a atuação de órgãos de gestão pública e ambiental nos mais variados níveis: municipal estadual e federal. Além destes, registra-se também a participação da sociedade civil, em especial, dos pescadores artesanais de Paraty e de suas representações, na busca pelo tratamento dos conflitos nos quais estão inseridos. Por outro lado, evidencia-se a falta de articulação e integração entre as políticas e atores, bem como entre as experiências institucionais em curso. Portanto, um dos maiores desafios existentes na implantação de um modo compartilhado de gestão dos recursos pesqueiros na BIG consiste justamente em superar tais limitações institucionais, de maneira que possam promover ações articuladas visando não apenas a conservação integrada do ecossistema, como também a reprodução das práticas tradicionais de pesca e a sua co-existência com os demais tipos de usos

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This study summarizes previously published and updated empirical relations for the estimation of production/biomass ratios in benthic invertebrates; of natural mortality in benthic invertebrates and finfish; and of respiration from production and vice versa in animal populations. AMS-EXCEL spreadsheet containing these equations is available from the author via Email. They are also included in the Ecopath with Ecosim software.

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A brief review of the status of the ECOPATH modeling approach and software is presented, with emphasis on the recent release of a Windows version (ECOPATH 3.0), which enables consideration of uncertainties, and sets the stage for simulation modeling using ECOSIM. Modeling of coral reefs is emphasized.

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The article provides insights on agroecosystem modeling and analysis with ECOPATH II.

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A discussion is presented on the topic of statistical data analysis in the field of ecology, emphasizing the importance of computer programmes being user friendly for the ecologist. Particular reference is given to TWINSPAN, CANOCO and PATN and the applications of these programmes to tropical fisheries and coastal zone management.

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The article highlights the scope for growth of aquaculture and the importance of new knowledge and skills for aquaculture to expand, become more productive and sustainable.

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Fishing is widely recognized to have profound effects on estuarine and marine ecosystems (Hammer and Jansson, 1993; Dayton et al., 1995). Intense commercial and recreational harvest of valuable species can result in population collapses of target and nontarget species (Botsford et al., 1997; Pauly et al., 1998; Collie et al. 2000; Jackson et al., 2001). Fishing gear, such as trawls and dredges, that are dragged over the seafloor inflict damage to the benthic habitat (Dayton et al., 1995; Engel and Kvitek, 1995; Jennings and Kaiser, 1998; Watling and Norse, 1998). As the growing human population, over-capitalization, and increasing government subsidies of fishing place increasing pressures on marine resources (Myers, 1997), a clear understanding of the mechanisms by which fishing affects coastal systems is required to craft sustainable fisheries management.

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In this note we describe the re-formation of a spawning aggregation of mutton snapper (Lutjanus analis). A review of four consecutive years of survey data indicates that the aggregation may be increasing in size. Mutton snapper are distributed in the temperate and tropical waters of the western Atlantic Ocean from Florida to southeastern Brazil (Burton, 2002). Juveniles and subadults are found in a variety of habitats such as vegetated sand bottoms, bays, and mangrove estuaries (Allen, 1985). Adults are found offshore on coral reefs and other complex hardbottom habitat. They are solitary and wary fish, rarely found in groups or schools except during spawning aggregations (Domeier et al., 1996). Spawning occurs from May through July at Riley’s Hump (Domeier et al., 1996) and peaks in June, as indicated by gonadosomatic indices (M. Burton, unpubl. data). Mutton snapper are highly prized by Florida fishermen for their size and fighting ability, and the majority of landings occur from Cape Canaveral, through the Florida Keys, including the Dry Tortugas (Burton, 2002).

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In the 1500’s, the waters of Venezuela and to a lesser extent Colombia produced more natural pearls than any place ever produced in the world in any succeeding century. Atlantic pearl-oysters, Pinctata imbricata Röding 1798, were harvested almost entirely by divers. The pearls from them were exported to Spain and other European countries. By the end of the 1500’s, the pearl oysters had become much scarcer, and little harvesting took place during the 1600’s and 1700’s. Harvesting began to accelerate slowly in the mid 1800’s and has since continued but at a much lower rate than in the 1500’s. The harvesting methods have been hand collecting by divers until the early 1960’s, dredging from the 1500’s to the present, and hardhat diving from 1912 to the early 1960’s. Since the mid 1900’s, Japan and other countries of the western Pacific rim have inundated world markets with cultured pearls that are of better quality and are cheaper than natural pearls, and the marketing of natural pearls has nearly ended. The pearl oyster fishery in Colombia ended in the 1940’s, but it has continued in Venezuela with the fishermen selling the meats to support themselves; previously most meats had been discarded. A small quantity of pearls is now taken, and the fishery, which comprised about 3,000 fishermen in 1947, comprised about 300 in 2002.