Environmental changes in Sepetiba Bay, SE Brazil

Sepetiba Bay is an example of an aquatic environment that has been severely impacted by human occupation and industrial activities in its basin. Some 400 industries including metallurgical, petrochemical and pyrometallurgical smelters, which emitted pollutants to air, soil and water, were established in Sepetiba Basin during the past 30 years. Apart from these point sources, changes in land use have also resulted in a large remobilization of pollutant deposition on Sepetiba Bay Basin. Studies have pointed out significant changes in sedimentation rates, concentrations of inorganic pollutants (Zn, Cd, Pb and Hg) and more recently, eutrophication, pointing to this area as an example of an impacted coastal zone. Notwithstanding local sources, Sepetiba Bay also suffers environmental impacts caused by diversion of river waters from adjacent basins, with some 30% of the total Hg flux to Sepetiba Bay and a 10-fold increase in water and sediment fluxes resulting from this. Decreasing environmental quality compromises both the large biodiversity and the potential economic uses of Sepetiba Bay, including fisheries and tourism. Monitoring of heavy metal levels in organisms (algae, mollusks, crustaceans and oysters) often shows concentrations well above the limits allowed following Brazilian legislation for food quality. Historical evolution of these concentrations suggests a worsening of the situation. Failure to monitor the effect of land-based activities, including those from other basins artificially associated with Sepetiba Bay has resulted in poor scenario construction and proper management planning.

[1]  C. S. Karez,et al.  Trace metal accumulation by algae in Sepetiba Bay, Brazil. , 1994, Environmental pollution.

[2]  L. Lacerda,et al.  Temporal and spatial variability in Zn, Cr, Cd and Fe concentrations in oyster tissues (crassostrea brasiliana lamarck, 1819) from Sepetiba Bay, Brazil , 1986 .

[3]  A. Lugo,et al.  LITTER PRODUCTION AND TURNOVER IN BASIN MANGROVE FORESTS IN SOUTHWEST FLORIDA , 1986 .

[4]  L. Lacerda,et al.  Heavy metal contamination of the marine biota along the Rio de Janeiro coast, SE-Brazil , 1991 .

[5]  L. Lacerda,et al.  Geochemical Characterization of Rain Water Particulate Material on a Coastal Sub-Tropical Region in SE: Brazil , 1998 .

[6]  L. Lacerda,et al.  Cadmium and zinc source assessment in the Sepetiba Bay and basin region , 1994, Environmental monitoring and assessment.

[7]  L. Lacerda,et al.  Effect of Root Metabolism on the Post-Depositional Mobilization of Mercury in Salt Marsh Soils , 1997, Bulletin of environmental contamination and toxicology.

[8]  Christovam Barcellos,et al.  Zn and Cd production and pollution in A Brazilian coastal region , 1991 .

[9]  L. Martinelli,et al.  The fate of trace metals in suspended matter in a mangrove creek during a tidal cycle , 1988 .

[10]  L. Lacerda,et al.  Relative Importance of Non-Point Sources of Mercury to an Industrialized Coastal System, Sepetiba Bay, SE Brazil , 1999 .

[11]  L. Lacerda Trace metals biogeochemistry and diffuse pollution in mangrove ecosystems , 1998 .

[12]  J. Nriagu,et al.  Quantitative assessment of worldwide contamination of air, water and soils by trace metals , 1988, Nature.

[13]  L. Lacerda,et al.  Mercury distribution and reactivity in waters of a subtropical coastal lagoon, Sepetiba Bay, SE Brazil , 2001 .

[14]  L. Lacerda,et al.  Dissolved mercury concentrations and reactivity in mangrove waters from the Itacurussa Experimental Forest, Sepetiba Bay, SE Brazil , 2001, Wetlands Ecology and Management.

[15]  M. Nishijo,et al.  Water Pollution by Cadmium and the Onset of Itai-itai Disease , 1992 .

[16]  L. Lacerda,et al.  Geochemistry of Mercury in Sediments of a Sub-Tropical Coastal Lagoon, Sepetiba Bay, Southeastern Brazil , 1998, Bulletin of environmental contamination and toxicology.