Abstract

Sediment capping with activated carbon (AC) is an effective technique used in remediation of contaminated sediments, but the ecological effects on benthic microbial activity and meiofauna communities have been largely neglected. This study presents results from a 4-week experiment investigating the influence of two powdered AC materials (bituminous coal-based and coconut shell-derived) and one control material (clay) on biogeochemical processes and meiofauna in contaminated sediments. Capping with AC induced a 62–63% decrease in denitrification and a 66–87% decrease in dissimilatory nitrate reduction to ammonium (DNRA). Sediment porewater pH increased from 7.1 to 9.0 and 9.7 after addition of bituminous AC and biomass-derived AC, respectively. High pH (>8) persisted for at least two weeks in the bituminous AC and for at least 24 days in the coconut based AC, while capping with clay had no effect on pH. We observed a strong impact (nitrate fluxes being halved in presence of AC) on nitrification activity as nitrifiers are sensitive to high pH. This partly explains the significant decrease in nitrate reduction rates since denitrification was almost entirely coupled to nitrification. Total benthic metabolism estimated by sediment oxygen uptake was reduced by 30 and 43% in presence of bituminous coal-based AC and coconut shell-derived AC, respectively. Meiofauna abundances decreased by 60–62% in the AC treatments. Taken together, these observations suggest that AC amendments deplete natural organic carbon, intended as food, to heterotrophic benthic communities. Phosphate efflux was 91% lower in presence of bituminous AC compared to untreated sediment probably due to its content of aluminum (Al) oxides, which have high affinity for phosphate. This study demonstrates that capping with powdered AC produces significant effects on benthic biogeochemical fluxes, microbial processes and meiofauna abundances, which are likely due to an increase in porewater pH and to the sequestration of natural, sedimentary organic matter by AC particles.

Highlights

  • Sediments represent the largest ecosystem on Earth in spatial coverage and metabolize large amounts of settling organic matter and pollutants through the activity of living benthic macro- and microorganisms (Atlas, 1981; Middelburg et al, 1993)

  • Results from sediment core incubation experiments showed that activated carbon (AC) capping had a significant impact on the main nitrate reduction pathways, i.e., denitrification and dissimilatory reduction to ammonium (DNRA)

  • The overall reduction in nitrate effluxes at the sediment water interface in spite of the decrease in the main nitrate removal processes in the sediment further indicates that nitrification activity was inhibited by AC capping

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Summary

Introduction

Sediments represent the largest ecosystem on Earth in spatial coverage and metabolize large amounts of settling organic matter and pollutants through the activity of living benthic macro- and microorganisms (Atlas, 1981; Middelburg et al, 1993). Oxygen and nitrate are the most valuable electron acceptors for organic matter degradation (Canfield et al, 2005). Most of benthic microbes are confined to surface sediments, where oxygen and nitrate are available and organic matter quality and quantity peaks. Inorganic compounds such as nitrate, ammonium, phosphate and silicate are products of microbial degradation of organic matter and may be either sequestered in the sediment by geochemical processes, or be released to the water column and assimilated as nutrients by microorganisms and primary producers and be retained in the food web.

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