Abstract
Benthic foraminifera were sampled monthly during a one-year period in order to examine their biological response to the environmental factors in the Ubatuba Bay (northern coast of Sao Paulo State, Brazil). The area is a popular tourist destination with a population that varies during the year, as does the untreated sewage carried into the bay by the rivers. Four sites were analysed. Each station is near one of the rivers that discharge into the bay. Biological data were analysed with multivariate and univariate techniques. The influence of the abiotic parameters on the foraminiferal fauna was inferred through statistical methods and time correlation functions. Geochemical and populational parameter differences allowed the sites to be separated into two groups according to their stress conditions. One group was dominated by Ammonia tepida —a herbivore species—and showed higher densities indicating a more productive and less contaminated location. The other one was dominated by Buliminella elegantissima —a detritivore species. Species diversity did not seem to be a good indicator of environmental health in this area due to the low densities and the high dominance of few species. Nevertheless, density and richness were used as evidence of local productivity and environmental conditions. Quasi-azoic moments related to the high degree of contamination were observed. Anthropogenic effects were stronger in the austral summer period, when sewage input through the rivers increases due to mass tourism.
Highlights
In coastal ecosystem sediment, the contaminants that are derived from human activities usually reach concentrations capable of causing adverse biological effects
The Ubatuba Bay is situated on the northern coast of São Paulo State, Brazil (23°25’-23°27’S and 45°01’-45°03 ́W), forming an area of approximately 8 km2
The lowest values were registered at Station 50, as a consequence of the Grande de Ubatuba River which, among the four tributary bay rivers, has the highest river discharge
Summary
The contaminants that are derived from human activities usually reach concentrations capable of causing adverse biological effects. As a rule, urbanised littoral areas receive effluent discharges, resulting in the contamination of water, sediment and the biota. This in turn may affect human health either by direct contact or through the food chain. Bottom sediments are a source of nutrients for the water column above them, leading to benthic-pelagic coupling and influencing primary productivity (Jorgensen, 1996). Sediments may act either as a sink or as a source of contaminants in these ecosystems
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