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Elsey-Quirk Et Al 2019.Pdf Estuarine, Coastal and Shelf Science 221 (2019) 170–183 Contents lists available at ScienceDirect Estuarine, Coastal and Shelf Science journal homepage: www.elsevier.com/locate/ecss Mississippi river sediment diversions and coastal wetland sustainability: Synthesis of responses to freshwater, sediment, and nutrient inputs T ∗ T. Elsey-Quirka, , S.A. Grahamb, I.A. Mendelssohna, G. Sneddenc, J.W. Daya, R.R. Twilleya, G. Shafferd, L.A. Sharpe, J. Pahlf, R.R. Laneg a Department of Oceanography and Coastal Sciences, Louisiana State University, Baton Rouge, LA, 70803, USA b Department of Biological Sciences, Nicholls State University, Thibodaux, LA, 70301, USA c U. S. Geological Survey, Wetland and Aquatic Research Center, Baton Rouge, LA, 70803, USA d Department of Biological Sciences, Southeastern Louisiana University, Hammond, LA, 70402, USA e Louisiana Coastal Protection and Restoration Authority, Lafayette, LA, 70596, USA f Louisiana Coastal Protection and Restoration Authority, Baton Rouge, LA, 70802, USA g Comite Resources Inc., P.O. Box 66596, Baton Rouge, LA, 70896, USA ARTICLE INFO ABSTRACT Keywords: Management and restoration of coastal wetlands require insight into how inundation, salinity, and the avail- Restoration ability of mineral sediment and nutrients interact to influence ecosystem functions that control sustainability. Decomposition The Mississippi River Delta, which ranks among the world's largest and most productive coastal wetland com- Productivity plexes, has experienced extensive deterioration over the last century due, in large part, to enhanced vulnerability Eutrophication to relative sea-level rise and lateral erosion caused by a combination of natural processes and anthropogenic Accretion modifications of hydrology. This land loss crisis has prompted the State of Louisiana to develop a comprehensive Mississippi delta restoration plan that includes constructing and implementing a series of large-scale sediment diversions that will reconnect sediment- and nutrient-rich Mississippi River water to adjacent bays, estuaries, and wetlands. Sediment loading through diversions is predicted to enhance the long-term sustainability of coastal wetlands; however, the additive effects of increased inundation, abrubt changes in the salinity regime, and high nutrient loads on wetland plant growth and organic matter (SOM) decomposition rates, which help regulate accretion and elevation change, is uncertain. Therefore, this review attempts to synthesize existing information to inform predictions of the interactive effects of diversions on these drivers of coastal wetland sustainability. The data suggest that sediment deposition within an optimal elevation range will increase the overall productivity of existing wetlands where prolonged flooding does not counter this effect by limiting plant growth. A reduction in salinity may increase plant productivity and cause vegetation shifts to less salt tolerant species, but seasonal swings in salinity may have unforeseen consequences. Nutrient-loading is predicted to lead to greater above- ground productivity, which, in turn, can facilitate additional sediment trapping; however, belowground pro- ductivity may decline, particularly in areas where sediment deposition is limited. In areas experiencing net deposition, nutrient-enrichment is predicted to enhance belowground growth into new sediment and contribute to positive effects on soil organic matter accumulation, accretion, and elevation change. Thus, we contend that sediment input is essential for limiting the negative effects of flooding and nutrient-enrichment on wetland processes. These conclusions are generally supported by the biophysical feedbacks occurring in existing pro- grading deltas of the Mississippi River Delta complex. 1. Introduction transformation and removal, burial and long-term sequestration of carbon, and storm surge protection for coastal communities (e.g., Coastal wetlands are among the most productive ecosystems on the Boesch and Turner, 1984; Chmura et al., 2003; Costanza et al., 2008; planet, performing ecological functions that contribute to services of Sousa et al., 2010; Batker et al., 2014). Yet despite their high value, high economic value such as habitat for fish and wildlife, nutrient coastal wetlands around the world are experiencing a convergence of ∗ Corresponding author. E-mail address: [email protected] (T. Elsey-Quirk). https://doi.org/10.1016/j.ecss.2019.03.002 Received 6 September 2018; Received in revised form 25 February 2019; Accepted 4 March 2019 Available online 09 March 2019 0272-7714/ © 2019 Elsevier Ltd. All rights reserved. T. Elsey-Quirk, et al. Estuarine, Coastal and Shelf Science 221 (2019) 170–183 human disturbance and sea-level rise that threatens their long-term new land through restoration is of both ecological and economic im- sustainability. The world's river deltas are particularly vulnerable to portance. rapid environmental change due to the combined effects of river In an attempt to offset widespread and rapid coastal land loss, the management and natural processes on flooding regime, sediment Coastal Protection and Restoration Authority (CPRA) of Louisiana has supply, salinity, and nutrient loading, which regulate complex feed- developed, revised, and expanded three Coastal Master Plans (CMPs; backs among plant community composition and productivity, organic CPRA, 2007, 2012 and 2017). The most recent CMP outlines plans for matter decomposition, and soil accretion. Coastal wetland manage- 79 restoration projects designed to build or maintain approximately ment, therefore, requires an understanding of how these hydro- 2000 km2 of land through a combination of wetland creation, sediment geomorphic factors interact to influence wetland stability and resilience diversions, and barrier island restoration (CPRA, 2017). More specifi- to sea-level rise and other stressors (Kirwan and Megonigal, 2013). cally, the 2017 CMP proposes seven large-scale sediment diversion In the Mississippi River delta, as in deltas around the world, wet- projects to be implemented over the next 50 years (Pahl et al., 2019 this lands form as vegetation colonizes subaerial sediments deposited in volume). River sediment diversions are engineered outlets through shallow coastal environments. Historically, the Mississippi River and its existing levees designed for periodic and/or sustained delivery of distributaries freely overflowed their banks and penetrated natural le- freshwater, nutrients, and sediment to create new wetlands and combat vees as crevasse splays during periods of high flow creating a delta- further degradation (Day et al., 2007; CPRA, 2017; Peyronnin et al., complex made up of several hydrologic basins separated by active or 2017). Once diversion structures are operational, water flows from the abandoned distributary ridges (Roberts, 1998; Day et al., 2000; Blum river by gravity and is distributed to the receiving basin largely by and Roberts, 2012). Eight major delta lobes have been identified in- wind, waves, tides and currents. In essence, diversions are designed to cluding the Atchafalaya, which is in the early stages of development. mimic natural crevasse splays and promote sub-delta development Each delta lobe, having a lifespan of approximately 1500 years and (Davis, 2000). In total, coastal restoration and protection efforts in covering 100s–1000s of km2, formed as river channels elongated and Louisiana represent the largest ever attempt to restore a natural system, bifurcated. Delta lobes are ultimately abandoned through a process of with an estimated cost of $50 billion over 50 years. upstream avulsion in favor of shorter, more efficient routes to sea level. The high cost and scale of the proposed coastal restoration in the Even after abandonment, most distributaries continued to flow with Mississippi River Delta necessitates improved predictions of how sedi- river water during major floods, maintaining a framework of inter- ment diversions will change important environmental drivers that in- connected distributary channels and natural levee ridges (Penland teract to influence key wetland processes. In this context, our goal was et al., 1988), and extending the life of wetlands in abandoned delta to synthesize existing information on the effects of flooding, freshwater lobes until their ultimate degradation. Numerous crevasses also func- input, nutrient, and mineral sediment availability on processes that tioned at a smaller scale during high water for a few years to as long as influence coastal wetland sustainability, including plant productivity, a century to build sediment splays adjacent to the natural levee with decomposition, and rates of accretion and elevation change, as well as areas of 10s–100s of km2 (Saucier, 1963; Weller, 1959; Davis, 2000; discuss likely interactions. Finally, we summarize our findings, with Roberts, 1998; Shen et al., 2015). The discharge of mineral sediment support from case studies where rivers flow freely into receiving basins, during delta formation or through crevasse splays created elevations to help better understand the fate of coastal wetlands receiving diverted appropriate for wetland vegetation to colonize and facilitated positive river wate and sediment. While this review is broadly applicable, our feedbacks among primary productivity, organic matter accumulation, focus is on potential changes to wetland plant productivity, organic sediment-trapping, and accretion following plant establishment. matter decomposition, accretion and elevation change that are
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