Percurso pedestre no Rio Este: contribuição para a educação ambiental e promoção do ensino experimental

O ensino praticado nas nossas escolas necessita ser mais consentâneo com os princípios e valores veiculados pela Educação Ambiental. Pretende-se, com este trabalho, levar os alunos a percepcionar a natureza com um olhar diferente, a estabelecer uma nova relação com o meio, adoptando uma postura pró-activa na defesa do espaço ribeirinho. Por meio de um percurso investigativo ao longo da margem esquerda de um troço do rio Este, na zona envolvente da Escola, os alunos de uma turma do 5º ano estudaram a flora autóctone existente na zona ribeirinha e recolheram amostras de água onde puderam aplicar processos de tratamento. Os temas abordados pertencem aos conteúdos leccionados nas aulas de Ciências da Natureza. Considerando que estas actividades podem ser importantes ferramentas na educação para o ambiente, elaborou-se para o grupo experimental um caderno de campo, que serviu de orientação ao estudo da flora, realizou-se uma actividade prática no laboratório, com a amostra da água recolhida. Posteriormente aplicou-se um teste, para conhecer o grau de conhecimento adquirido após a actividade e, no final, os alunos responderam a um inquérito para se conhecer o seu grau de satisfação. Ainda que os resultados do teste não mostrem diferenças significativas na aquisição de conhecimento em relação à turma não participante no projecto, a interpretação da paisagem mostrou-se um meio eficaz de envolver os alunos, desenvolver sensibilidades, construir conceitos, promover atitudes positivas que vão de encontro a uma Educação Ambiental ligada à cidadania.

Lipid content and fatty acid profile of Senegalese sole (Solea senegalensis Kaup, 1858) juveniles as affected by feed containing different amounts of plant protein sources

A growth trial with Senegalese Sole (Solea senegalensis Kaup, 1858) juveniles fed with diets containing increasing replacement levels of fishmeal by mixtures of plant protein sources was conducted over 12 weeks. Total fat contents of muscle, liver, viscera, skin, fins and head tissues were determined, as well as fatty acid profiles of muscle and liver (GC-FID analysis). Liver was the preferential local for fat deposition (5.5–10.8% of fat) followed by fins (3.4–6.7% fat). Increasing levels of plant protein in the diets seems to be related to increased levels of total lipids in the liver. Sole muscle is lean (2.4–4.0% fat), with total lipids being similar among treatments. Liver fatty acid profile varied significantly among treatments. Plant protein diets induced increased levels of C16:1 and C18:2 n -6 and a decrease in ARA and EPA levels. Muscle fatty acid profile also evidenced increasing levels of C18:2 n 6, while ARA and DHA remained similar among treatments. Substitution of fishmeal by plant protein is hence possible without major differences on the lipid content and fatty acid profile of the main edible portion of the fish – the muscle.

An uncertainty and sensitivity analysis applied to the prioritisation of pharmaceuticals as surface water contaminants from wastewater treatment plant direct emissions

In this study, the concentration probability distributions of 82 pharmaceutical compounds detected in the effluents of 179 European wastewater treatment plants were computed and inserted into a multimedia fate model. The comparative ecotoxicological impact of the direct emission of these compounds from wastewater treatment plants on freshwater ecosystems, based on a potentially affected fraction (PAF) of species approach, was assessed to rank compounds based on priority. As many pharmaceuticals are acids or bases, the multimedia fate model accounts for regressions to estimate pH-dependent fate parameters. An uncertainty analysis was performed by means of Monte Carlo analysis, which included the uncertainty of fate and ecotoxicity model input variables, as well as the spatial variability of landscape characteristics on the European continental scale. Several pharmaceutical compounds were identified as being of greatest concern, including 7 analgesics/anti-inflammatories, 3 β-blockers, 3 psychiatric drugs, and 1 each of 6 other therapeutic classes. The fate and impact modelling relied extensively on estimated data, given that most of these compounds have little or no experimental fate or ecotoxicity data available, as well as a limited reported occurrence in effluents. The contribution of estimated model input variables to the variance of freshwater ecotoxicity impact, as well as the lack of experimental abiotic degradation data for most compounds, helped in establishing priorities for further testing. Generally, the effluent concentration and the ecotoxicity effect factor were the model input variables with the most significant effect on the uncertainty of output results.