Abstract

To establish the environmental status of Rufiji coastal waters in Tanzania, it is necessary to document the different contaminants as major entry points into the lower estuarine areas. Because there is no data on polycyclic aromatic hydrocarbon (PAH) contamination in this estuarine delta, the current study measured the concentrations of 19 PAHs in suspended particulate matter (SPM), surface sediments and marine organisms that are part of a telescoping food chain (gastropod Terebralia sp., clams Crassostrea cucullata, crabs Uca sp., panaeid shrimps Panaeus monodon, teleost Hilsa kelee, Trichiurus lepturus, and Arius thalassinus). Total PAH concentrations in SPM were low to moderate (18.7–223 ng/g) and varied between the sites; phenanthrene and chrysene were the dominant PAHs (2.40–47.2 and 4.20–28.1 ng/g, respectively). Significant variation between the sites indicates the influence of fuel spills and contribution from terrestrial sources resulting from different land use practices, such as agriculture, fishing, and harvesting firewood, charcoal, and mangroves poles. PAH concentrations in surface sediments were higher (127–376 ng/g) than SPM samples, and high molecular weight PAHs were the dominant fraction. Animal tissues indicated low PAH levels (9.20–158 ng/g). Only low molecular weight PAHs were dominant in the muscle tissues of pelagic and filter feeders (C. cucullata, P. monodon, and H. kelee). Bioaccumulation factor (BAF) ranged between 0.20 and 69.5 and it suggests 1) PAH accumulation in the marine organisms has so far been limited, and 2) distribution of PAHs in the Rufiji estuary poses limited risks.

Highlights

  • Estuarine areas are of substantial ecological, environmental, and economic value to the coastal and inland communities

  • Sampling site 1 showed significantly (p < 0.05) low concentration of total Polycyclic aromatic hydrocarbons (PAHs) compared to sites 2 and 3, but there were no significant differences between sites 2 and 3

  • The total concentration of potentially carcinogenic PAHs which include benzo[a]anthracene, chrysene, benzo[b]fluoranthene, benzo[k]fluoranthene, benzo[a]pyrene, indeno[1,2,3-c,d]pyrene, and dibenzo[a,h]anthracene (International Agency for Research on Cancer, 1987) ranged from 5.70 to 59.4 ng/g, with site 3 showing significantly (p < 0.005) higher concentration compared to site 1

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Summary

Introduction

Estuarine areas are of substantial ecological, environmental, and economic value to the coastal and inland communities. The different habitats and high rates of primary production in estuaries allow them to be home to a diversity of plant and animal life that support fishing, aquaculture, tourism and recreation (Sørensen, 1998; Elliott and Whitfield, 2011). These activities constitute the main sources of livelihood and income to the local communities. Climate which plays an important role in precipitation, flooding events, and driving various human activities is an important driver of both natural and anthropogenic changes in estuaries These changes for example influence the distribution of various organic and inorganic pollutants that impact the flora and fauna in these sensitive and dynamic ecosystems

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