993 resultados para Biotic Index Sludge


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Protozoan were collected from 16 stations in water system of Changde City (China) using the PFU method. Sampling programs were conduced on a yearly basis, with seasonal frequency at diverse sites in the water system and 488 species of protozoa was identified. At the same time, Water sampling from these stations was conducted and various water chemical parameters, including DO, COD, BOD5, NH3, TP, and Volatile Phenol, were analyzed. The aim of the research was, on one hand, using chemical method to take an investigation to the water pollution status of Changde City; on the other hand, using protozoan to make an evaluation to the water quality. With the chemical water parameters and protozoa data, a biotic index was derived for the investigated region. The species pollution value (SPV) of 469 protozoa species was established, and the community pollution value (CPV) calculated from SPV was used to evaluate water quality. The method of the biotic index was tested and the result showed that CPV calculated from SPV had a close correlation with the degree of water pollution (p < 0.00001). This indicated that the method of the biotic index is reliable. The water quality degrees divided by CPV were suggested. (c) 2004 Elsevier B.V. All rights reserved.

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A method of comparing data on protozoan communities with chemical parameters is presented. Using data from an extensive survey of the River Hanjiang in China, each species of protozoa has been given a species pollution value (SPV) related to its occurrence in waters with different degrees of pollution. A comprehensive chemical index is calculated for each site based on water quality standards for eight chemical parameters. The index is calculated from the relationship between the observed levels of each chemical at a site, compared with the limits of the drinking water quality standards of the People's Republic of China. From the distribution of each species at sites with differing chemical index values, a SPV is calculated. The SPV for each species is obtained by summing the logarithmic value of 10 times the chemical pollution divided by the number of chemical parameters, then divided by the stations where the species occurs. The community pollution value (CPV), which is the average SPVs of all protozoa at a site, is used to evaluate water quality. The CPV has been shown to have a close correlation with the degree of water pollution. It is not necessary for all the protozoa in a sample to have SPVs listed in this paper, provided at least 56% of the protozoa in a sample have an SPV value, the CPV will be applicable.

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Protozoans of Lake Donghu were collected from five stations using the PFU method. The sampling was conducted for one year and two times a month. The aim of this research was to test the applicability of a new protozoa biotic index, species pollution value (SPV) and community pollution value (CPV), established by the authors using data from the River Hanjiang. Each station's CPV was calculated from the SPV and the correlation analysis between the CPV and the comprehensive chemical index of stations I, II, III showed a significant correlation between them. The pollution status of the five stations was correctly evaluated by the CPV. These results suggested that the biotic index could be applied in water systems other than the River Hanjiang. The SPV of some protozoa species in Lake Donghu, not observed in the River Hanjiang were established. In order to further test the applicability of the biotic index, protozoan and chemistry data from the Rivers Torrente Stirone and Parma of Italy were used. The results showed that the CPV for the two rivers had a close relationship with the chemical water quality, which indicated that the biotic index could be applied in other parts of the world for the monitoring and estimating of water quality. Since the results of testing and verifying the biotic index in some other water systems in China were also satisfactory, this indicated that the biotic index has an extensive suitability for freshwater ecosystems. As long as more than 50% of the species in a sample have a SPV, the CPV calculated from the SPV is reliable for monitoring and evaluating water quality.

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O aumento da concentração de nutrientes nos corpos receptores, principalmente nitrogênio e fósforo oriundos de efluentes sanitários e industriais pode gerar o fenômeno da eutrofização. Para que isto não ocorra é necessário que este efluente passe por um tratamento adequado, no entanto, o papel desempenhado por diversos grupos de microrganismos encontrados nos sistemas de tratamento de efluentes não é completamente compreendido devido à complexidade das interações. Este trabalho teve como objetivo caracterizar a estrutura e dinâmica da comunidade microbiana (bactérias envolvidas no ciclo do nitrogênio e microfauna) e avaliar a atividade biológica dos reatores aeróbio e anaeróbio de uma indústria de alimentos. Os parâmetros físico-químicos da estação de tratamento foram monitorados, bem como foi feita a avaliação da estrutura e dinâmica da comunidade bacteriana envolvida no ciclo do nitrogênio por meio da técnica de Hibridização in situ Fluorescente. A microfauna do reator aeróbio foi caracterizada e classificada conforme o Índice Biótico do Lodo. A atividade biológica do lodo foi avaliada através do Teste de Respirometria e foram feitas correlações entre a microbiota encontrada no reator aeróbio e parâmetros físico-químicos. Os parâmetros físico-químicos analisados estiveram dentro dos limites permitidos pelas legislações federais e estaduais e os parâmetros Demanda Bioquímica de Oxigênio, Demanda Química de Oxigênio e Nitrogênio Kjeldahl foram reduzidos de 99,8%, 99,6% e 74,9%, respectivamente. Foi possível observar a presença tanto de bactérias oxidadoras de nitrito quanto de amônia em ambos os reatores analisados, bem como em cada ponto de coletas dentro dos reatores. A bactéria Pseudomonas fluorescens também ocorreu em todos os pontos de coleta dos dois reatores. Dentre os grupos que compõem a microfauna do lodo ativado, os ciliados rastejantes foram os mais frequentes, seguido pelas tecamebas, rotíferos, ciliados sésseis, ciliados livre natantes, flagelados e outros invertebrados. Além disso, não houve diferença entre as densidades dos grupos encontradas nos Pontos 1 e 2 do reator aeróbio e o Índice Biótico do Lodo encontrado foi igual a 8 (classe I). A semelhança apresentada entre a Taxa de Consumo de Oxigênio dos pontos 1 e 2, bem como a Taxa de Consumo de Oxigênio específica entre os pontos 1 e 2 sugere que o oxigênio é distribuído de forma homogênea dentro do tanque de aeração, fazendo com que os microrganismos tenham condições semelhantes de crescimento. Os ciliados livre natantes apresentaram correlação positiva com a DQO e DBO5 e os ciliados sésseis apresentaram correlação negativa com a DQO e com a DBO5. Os rotíferos apresentaram correlação negativa com Sólidos Suspensos Voláteis do reator aeróbio. Os ciliados rastejantes, tecamebas e rotíferos apresentaram correlação positiva com a microfauna total encontrada no reator aeróbio. Os ciliados livre natantes apresentaram correlação negativa com os ciliados sésseis, bactérias totais, Nitrobacter e outras bactérias; e correlação positiva com outros invertebrados. Os flagelados apresentaram correlação negativa com as bactérias totais, enquanto as outras bactérias apresentaram correlação positiva. Os outros invertebrados apresentaram correlação negativa com Nitrobacter.

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O processo de lodos ativados consiste em um tratamento biológico amplamente utilizado nas estações de tratamento, para remoção de matéria orgânica, devido à qualidade do efluente ao final do processo. Essa remoção é realizada por microrganismos que atuam neste sistema como bactérias, protozoários, metazoários e organismos filamentosos, como fungos e bactérias, formadores de flocos biológicos. Para garantir a eficiência deste processo deve haver um equilíbrio da microbiota dentro do reator aeróbio e o controle do número de filamentosos, tendo em vista que seu excesso no sistema pode causar o intumescimento do lodo (bulking) interferindo na qualidade do efluente gerado. O presente estudo teve como objetivo testar a eficiência de uma solução de 0,001% de peróxido de hidrogênio (H2O2) no controle de microrganismos filamentosos em lodos provenientes de duas indústrias, farmacêutica e alimentícia, reduzindo assim os riscos relacionados à utilização desta substância em grandes volumes. Foram realizadas análises microscópicas do lodo para avaliação quantitativa e monitoramento da atividade biológica dos reatores, essa avaliação serviu como base para a análise qualitativa a partir do índice de Madoni (1994) gerando um Índice Biótico do Lodo (IBL). Foram realizados outros testes, como IVL e teste de respiração, sendo os resultados destes testes comparados a fim de avaliar a eficiência da solução de H2O2 e sua interferência no processo. A solução de H2O2 foi eficiente em ambos os experimentos, mostrando através dos testes de TCO e TCOe não haver interferência desta solução no metabolismo da microfauna; os resultados do IBL mostraram uma boa qualidade do lodo para ambos experimentos e a partir desta análise foi observado que a elevação de temperatura, acima de 30,0C, causa interferência no sistema levando a uma redução do IBL. Os resultados de IVL não demonstraram diferença entre os valores dos reatores controle e tratado, porém a avaliação do tamanho dos flocos e filamentos mostrou que o aumento na concentração da solução de H2O2 levou a um controle na quantidade de filamentosos nos reatores tratados que reduziram em tamanho e quantidade.

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Biotic indices have been developed to summarise information provided by benthic macroinvertebrates, but their use can require specialized taxonomic expertise as well as a time-consuming operation. Using high taxonomic level in biotic indices reduces sampling processing time but should be considered with caution, since assigning tolerance level to high taxonomic levels may cause uncertainty. A methodology for family level tolerance categorization based on the affinity of each family with disturbed or undisturbed conditions was employed. This family tolerance classification approach was tested in two different areas from Mediterranean Sea affected by sewage discharges. Biotic indices employed at family level responded correctly to sewage presence. However, in areas with different communities among stations and high diversity of species within each family, assigning the same tolerance level to a whole family could imply mistakes. Thus, use of high taxonomic level in biotic indices should be only restricted to areas where homogeneous community is presented and families across sites have similar species composition.

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This is the Biological survey of River Teign and tributaries with references to the discharge of ball clay wastes, document produced by South West Water Authority in 1973. This report focuses on on-site assessment of the benthic macro-invertebrates of the lower River Teign, River Bovey, Ugbrooke Stream and Blatchford Brook was undertaken on 19th and 22nd August 1977 to assess the effects of discharges from ball clay mining premises. Inspection of aquatic fauna in the field is of necessity, less extensive than laboratory identification of sorted samples, so that the resulting data underestimates the water quality. This is more pronounced in the Chandler Score than in the Trent Biotic Index which does not take account of species abundance. Chandler should thus be interpreted by the trends described rather than by absolute values calculated.

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A study on the benthic ecosystem health was performed to assess the environmental quality of Montevideo coastal zone, in view of the construction of a new sanitation system. Data were compared to previous research undertaken 10 years ago, and biochemical composition of organic matter, heavy metals, organic matter, phytopigments, benthic diatoms, macrofauna community structure and a biotic index (AMBI) were used as proxies. Results indicate an environmental quality-gradient, with the worst conditions within the inner stations of Montevideo Bay and an improvement towards the adjacent coastal zone. Higher levels of chromium, lead, phaeopigments, organic biopolymers and poor benthic macrofauna and diatom communities, characterised the hypertrophic innermost portion of Montevideo Bay. Data indicated a clear deterioration of the adjacent coastal zone comparatively to that observed 10 years ago. The complementary use of approaches not applied before (benthic diatoms and organic biopolymers) with those formerly applied improve our assessment of the trophic status and the environmental health of the area. (C) 2010 Elsevier B.V. All rights reserved.

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The biomonitoring technique for water quality in water bodies has been incorporated increasingly in management of the natural resources, using mainly indices of its aquatic community characteristics. In Brazil the first efforts to use this technique was restricted to the South and the Midwest region of this country. Located in the northeast region, this study was conducted at Rio Grande do Norte state and had as main objective the assessment of water quality in the Piranhas-Açu river using benthic macroinvertebrates community as biological indicators. Thus, were applied two biotic indices, the BMWP (Biological Monitoring Working Party score system) and the IBF (Family Biotic Index). According the requirements of these indices, two periods of sampling were determined as basic methodology, in dry seasons of 2006 and 2007. The sampling sites were around the municipalities of Açu, Ipanguaçu, Alto do Rodrigues and Pendências. Physical-chemical measurements; a protocol of rapid assessment of diversity of habitats, and determination of the degree of tolerance of each taxon to organic pollution were also performed. The most abundant organisms found in the river were tolerant with the prevalence of Chironomidae (Diptera) and Melanoides tuberculata. This results, together with those ones got in indices application, showed a considerable organic pollution in the four sample places and the reaches were classified as modified to impacted. According to the used indices, this study suggest that this river have significant alteration in the biotic community and water quality on the organic pollution, and this fact, occurs in the reach of the river further downstream, where were expected a good water quality. Considering these results, measures aiming the conservation of this water body are needed regarding as it is inserted into a fragile ecosystem with dry season phenomenon, and the water of this river has extremely importance for the local economy

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

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The injection of gas into sub-seabed aquifers may lead to the displacement of hypoxic and hypersaline fluids (reservoir formation water) major environmental risk. To investigate this risk, the impact of formation water release on the macrofaunal community in a mesocosm experiment at Solbergstrand was conducted. 20 boxcores were exposed to 4 treatments (high salinity, hypoxic, mixed and tidal) during two weeks. The abundance of macrofauna was quantified for each treatment and richness, eveness and biodiversity indices calculated. The data are reported in this dataset.

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Knowledge of how biota can be used to monitor ecosystem health and assess impacts by human alterations such as land use and management measures taken at different spatial scales is critical for improving the ecological quality of aquatic ecosystems. This knowledge in Uganda is very limited or unavailable yet it is needed to better understand the relationship between environmental factors at different spatial scales, assemblage structure and taxon richness of aquatic ecosystems. In this study, benthic invertebrate community patterns were sampled between June 2001 and April 2002 and analysed in relation to water quality and catchment land use patterns from three shallow near-shore bays characterized by three major land uses patterns: urban (Murchison Bay); semi-urban (Fielding Bay); rural (Hannington Bay). Variations in density and guild composition of benthic macro-invertebrates communities were evaluated using GIS techniques along an urban-rural gradient of land use and differences in community composition were related to dissolved oxygen and conductivity variation. Based on numerical abundance and tolerance values, Hilsenhoff's Biotic Index ofthe invertebrates was determined in order to evaluate the relative importance of water quality in the three bays. Murchison Bay supported a relatively taxa-poor invertebrate assemblage mainly comprising stenotopic and eurytopic populations of pollution-tolerant groups such as worms and Chironomus sp. with an overall depression in species diversity. On the contrary, the communities in Fielding and Hannington bays were quite similar and supported distinct and diverse assemblages including pollution-intolerant forms such as Ephemeroptera (mayflies), Odonata (dragonflies). The Hilsenhoff Biotic Index in Murchison Bay was 6.53. (indicating poor water quality) compared to 6.34 for Fielding Bay and 5.78 for Hannington Bay (both indicating fair water quality). The characterization of maximum taxa richness balanced among taxa groups with good representation of intolerant individuals in Hannington Bay relative to Fielding and Murchison bays concludes that the bay is the cleanest in terms of water quality. Contrary, the dominance of few taxa with many tolerant iqdividuals present in Murchison Bay indicates that the bay is degraded in terms of water quality. These result are ofimportance when planning conservation and management measures, implementing large-scale biomonitoring programs, and predicting how human alterations (e.g nutrient loading) affect water ecosystems. Therefore, analysis of water quality in relation to macro-invertebrate community composition patterns as bio-indicators can lead to further understanding of their responses to environmental manipulations and perturbations.