Publications by authors named "A C R Albergaria-Barbosa"

Despite being one of the most remote areas on the planet, the Antarctic continent is subject to anthropogenic influences. The presence of various groups of contaminants, including persistent organic pollutants (POPs) and polycyclic aromatic hydrocarbons (PAHs), has been documented in the region over the past decades. However, a significant knowledge gap remains regarding the detection of new pollutants, such as emerging contaminants (ECs), in Antarctic coastal environments.

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The Brazil-Malvinas Confluence (BMC) is a significant biological frontier where distinct currents meet, fostering optimal conditions for phytoplankton development. In this study we tested the hypothesis that eddys promote an increase in phytoplankton biomass at the Brazil-Malvinas Confluence (BMC), altering species diversity. Phytoplankton were collected with Niskin bottles and nutrient concentrations assessed at two depths (Surface and Deep Chlorophyll Maximum Layer - DCML) in areas outside and under the influence of Cold-Core (CCE) and Warm-Core (WCE) Eddies.

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Plastic pellets represent a significant component of microplastic (< 5 mm) pollution. Impacts caused by plastic pellets involve physical harm and toxicity related to ingestion and non-ingestion (such as the release of chemicals in leachates). The latter is the main route of exposure for invertebrate macrobenthic populations.

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Article Synopsis
  • Untreated sewage increases nutrient levels and alters ecosystem functions, affecting the nitrogen isotopic signature (δN) in seagrasses.
  • Urbanization on Itaparica Island has led to minimal sewage treatment, risking further population growth and sewage input.
  • A study showed δN values in seagrass (Halodule wrightii) vary with urbanization, indicating potential anthropogenic pressure that could harm seagrass ecosystems despite some positive correlation with growth.
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This study aimed to evaluate B[a]P and low-density polyethylene microplastics (MPs) toxicty, alone and in mixture (0.03 to 30 μg L of B[a]P; and 5, 50 and 500 mg L for MPs). Five mg L of MPs is considerably higher than commonly reported environmental concentrations, although it has been reported for marine environments.

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