High nutrient loading to coastal bays is often accompanied by the presence of bloomforming macroalgae, which take up and sequester large amounts of C and N while growing. This pool is temporary, however, as nuisance macroalgae exhibit a bloom and die-off cycle, influencing the biogeochemical functioning of these systems in unknown ways. The objective of this study was to trace the C and N from senescing macroalgae into relevant sediment pools. A macroalgal die-off event was simulated by the addition of freeze-dried macroalgae (Gracilaria spp.), pre-labeled with stable isotopes ( 13 C and 15 N), to sediment mesocosms. The isotopes were traced into bulk sediments and partitioned into benthic microalgal (BMA) and bacterial biomass using microbial biomarkers to quantify the uptake and retention of macroalgal C and N. Bulk sediments took up label immediately following the die-off, and macroalgal C and N were retained in the sediments for at least 2 wk. Approximately 6 to 50% and 2 to 9% of macroalgal N and C, respectively, were incorporated into the sediments. Label from the macroalgae appeared in both bacterial and BMA biomarkers, suggesting that efficient shuttling of macroalgal C and N between these communities may serve as a mechanism for retention of macroalgal nutrients within the sediments.
KEY WORDS: Stable isotopes · Macroalgae · Benthic microalgae · Bacteria · Biomarker · Coastal eutrophication
Resale or republication not permitted without written consent of the publisherMar Ecol Prog Ser 414: [41][42][43][44][45][46][47][48][49][50][51][52][53][54][55] 2010 Studies of macroalgal bloom decay have demonstrated rapid breakdown of biomass, resulting in release of both inorganic and organic nutrients to the water column (Buchsbaum et al. 1991, Castaldelli et al. 2003, García-Robledo et al. 2008, supporting phytoplankton and bacterial metabolism , Nedergaard et al. 2002. Fewer studies have focused on macroalgal decay within the sediments (Nedergaard et al. 2002, Lomstein et al. 2006, Rossi 2007, García-Robledo et al. 2008, where heterotrophic bacterial densities are significantly higher than in the water column (Deming & Baross 1993, Schmidt et al. 1998, Ducklow 2000. In addition, most of the sediment studies have been conducted in low or no light environments, even though light is typically available to shallow sediments where macroalgal die-offs occur and sediment biogeochemistry is largely affected by benthic microalgal (BMA) activity (Underwood & Kromkamp 1999). While nutrients associated with senescent macroalgal blooms are recycled and can have a positive feedback on phytoplankton production in the water column, nutrients released during macroalgal decay in the sediments may support BMA and bacterial production, which could intercept the return of nutrients to the overlying water column. Thus if shallow-water sediments behave as a nutrient filter, the response by phytoplankton may be reduced, and benthic production could effectively buffer the system from further eutrophication. In order to be...