Literature DB >> 24689140

Effect of eastern oysters (Crassostrea virginica) on sediment carbon and nitrogen dynamics in an urban estuary.

Timothy J Hoellein, Chester B Zarnoch.   

Abstract

Oyster reefs have declined globally. Interest in their restoration has motivated research into oyster-mediated ecosystem services including effects on biodiversity, filtration, and nitrogen (N) cycling. Recent evidence suggests oysters may promote denitrification, or anaerobic respiration of nitrate (NO3-) into di-nitrogen gas, via benthic deposition of carbon (C) and N-rich biodeposits. However, the mechanisms whereby biodeposits promote N transformations prerequisite to denitrification (e.g., mineralization and nitrification) are unclear. Previous research has also not measured oysters' influence on N cycling in urbanized areas. In May 2010 we deployed eastern oysters (Crassostrea virginica) in mesh cages above sand-filled boxes at four sites across a nutrient gradient in Jamaica Bay, New York City (New York, USA). Oysters were arranged at four densities: 0, 40, 85, and 150 oysters/m2. For 17 months we measured water-column nutrients and chlorophyll a, every two weeks to monthly. Every two months we measured sediment ash-free dry mass (AFDM), exchangeable ammonium (NH4+), ammonification, nitrification, denitrification potential (DNP), and NO3- and C limitation of DNP. Oysters increased sediment AFDM at three of four sites, with the greatest increase at high density. Oysters did not affect any N pools or transformations. However, variation among sites and dates illustrated environmental drivers of C and N biogeochemistry in this urban estuary. Overall, nitrification was positively related to net ammonification, water column NH4+, and sediment NH4+, but was not correlated with DNP. Denitrification was consistently and strongly NO3- limited, while C was not limiting or secondarily limiting. Therefore, the oyster-mediated increase in AFDM did not affect DNP because C was not its primary driver. Also, because DNP was unrelated to nitrification, it is unlikely that biodeposit N was converted to NO3- for use as a denitrification substrate. Predicting times or sites where denitrification is driven by the C and N species originating from oyster biodeposits remains a challenge under eutrophic conditions. Towards this goal, we synthesized our conclusions with literature predictions in a conceptual model for pathways whereby oysters might influence C and N dynamics differently in oligotrophic relative to eutrophic ecosystems.

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Year:  2014        PMID: 24689140     DOI: 10.1890/12-1798.1

Source DB:  PubMed          Journal:  Ecol Appl        ISSN: 1051-0761            Impact factor:   4.657


  3 in total

1.  Growth, morphometrics, and nutrient content of farmed eastern oysters, Crassostrea virginica (Gmelin), in New Hampshire, USA.

Authors:  R E Grizzle; K M Ward; C R Peter; M Cantwell; D Katz; J Sullivan
Journal:  Aquac Res       Date:  2017-04       Impact factor: 2.082

2.  Opportunities and Challenges for Including Oyster-Mediated Denitrification in Nitrogen Management Plans.

Authors:  Julie M Rose; J Stephen Gosnell; Suzanne Bricker; Mark J Brush; Allison Colden; Lora Harris; Eric Karplus; Alix Laferriere; Nathaniel H Merrill; Tammy B Murphy; Joshua Reitsma; Johnny Shockley; Kurt Stephenson; Seth Theuerkauf; Dan Ward; Robinson W Fulweiler
Journal:  Estuaries Coast       Date:  2021-12       Impact factor: 2.976

3.  Drought-induced changes in flow regimes lead to long-term losses in mussel-provided ecosystem services.

Authors:  Caryn C Vaughn; Carla L Atkinson; Jason P Julian
Journal:  Ecol Evol       Date:  2015-02-25       Impact factor: 2.912

  3 in total

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