Abstract

Microorganisms and burrowing animals exert a pronounced impact on the cycling of redox sensitive metals in coastal sediments both spatially and temporally. In this study, we monitored the spatiotemporal dynamics of porewater and highly reactive solid phase iron with the corresponding prokaryotic and eukaryotic sedimentary microbial communities over one annual cycle from November 2015 to November 2016 in a bioturbated intertidal mudflat. Continuous and seasonally variable pools of both porewater Fe(II) and highly reactive iron (FeHR) were observed throughout the seasons with significant increases of Fe(II) and FeHR in response to increased sediment temperature in summer months. Maximum concentrations of Fe(II) and FeHR were predominantly confined to the upper 5 cm of sediment throughout the year. Iron-oxidizing and -reducing microorganisms were present and stable temporally, and exhibited a depth-dependent stratification likely due to availability of Fe(II) and FeHR pools, respectively. Zetaproteobacteria, presumptive lithotrophic iron-oxidizing bacteria, were present at abundances around 0.5 – 1% in the top five cm of sediment with decling abundance with depth. As a whole the microbial community was relatively stable across the seasons, and showed strongest separation with depth, probably driven by changes in oxygen availability and organic matter. The Deltaproteobacteria, principally taxa known to be associated with sulfur and iron cycling, were prevalent, especially at >5 cm depth. Gammaproteobacteria and Bacteroidetes were also abundant, with putatively aerobic members especially prevalent in the cm of the sediment. The relative abundance of diatoms, estimated from abundance of 18S rRNA gene counts, showed evidence of a seasonal signal possibly tied to spring and fall blooms. Overall, analysis of phytoplankton found significant abundance at depth, likely due to the feeding and bio-mixing activity of marine worms. Macro-, and meiofauna, consistent with expected taxa, were detected throughout the year via 18S gene counts, and showed some seasonal variations that may influence sedimentary iron transformations by active microbial grazing. In summary, this analysis revealed relatively consistent temporal and spatial trends in iron geochemistry and microbial and macrobial community composition, while also indicating a complex dynamic of microbial and macrobial interactions are responsible for maintaining these processes.

Highlights

  • Coastal marine sediments are active and dynamic environments that connect the flux of nutrients and energy from weathered land masses to marine ecosystems

  • Porewater Fe(II) concentrations peaked at a maximum average concentration of approximately 120 μmol L−1 at a depth interval between 3–4 cm, which is a consistent observation with many porewater Fe(II) profiles from coastal and continental shelf systems (Aller, 1980; Canfield, 1989; Hines et al, 1991; Thamdrup et al, 1994; Severmann et al, 2010; Antler et al, 2019), which are more often than not, bioturbated

  • The decline in Fe(II) with depth is likely due to the reaction with hydrogen sulfide produced by sulfate-reducing bacteria in sediments (Jørgensen, 1982) as well as around macrofaunal burrow walls (Bertics and Ziebis, 2010), which results in the precipitation of iron sulfides in sediments (Berner, 1984)

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Summary

Introduction

Coastal marine sediments are active and dynamic environments that connect the flux of nutrients and energy from weathered land masses to marine ecosystems. In addition to bio-irrigation, burrowing animals, principally marine worms in this case, physically mix sediments, which can act to transport organic matter and minerals within sediment layers Their burrow walls are hotspots for microbial redox cycling where steep geochemical gradients drive the rapid cycling between reduced and oxidized chemical species (Fenchel, 1969; Reichardt, 1986; Aller, 1994; Fenchel, 1996; Brune et al, 2000; Kristensen and Kostka, 2005; Bertics and Ziebis, 2009). Their complex burrowing and irrigating and bio-mixing behavior essentially increases the exchange of solutes between benthic and pelagic systems (Aller, 1982), and are of primary importance to benthic-pelagic coupling and ecosystem function (Griffiths et al, 2017)

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