Abstract

AbstractCoastal communities increasingly invest in natural and nature‐based features (e.g., living shorelines) as a strategy to protect shorelines and enhance coastal resilience. Tidal marshes are a common component of these strategies because of their capacity to reduce wave energy and storm surge impacts. Performance metrics of restoration success for living shorelines tend to focus on how the physical structure of the created marsh enhances shoreline protection via proper elevation and marsh plant presence. These metrics do not fully evaluate the level of marsh ecosystem development. In particular, the presence of key marsh bivalve species can indicate the capability of the marsh to provide non‐protective services of value, such as water quality improvement and habitat provision. We observed an unexpected low to no abundance of the filter‐feeding ribbed mussel, Geukensia demissa, in living shoreline marshes throughout Chesapeake Bay. In salt marsh ecosystems along the Atlantic Coast of the United States, ribbed mussels improve water quality, enhance nutrient removal, stabilize the marsh, and facilitate long‐term sustainability of the habitat. Through comparative field surveys and experiments within a chronosequence of 13 living shorelines spanning 2–16 years since construction, we examined three factors we hypothesized may influence recruitment of ribbed mussels to living shoreline marshes: (1) larval access to suitable marsh habitat, (2) sediment quality of low marsh (i.e., potential mussel habitat), and (3) availability of high‐quality refuge habitat. Our findings suggest that at most sites larval mussels are able to access and settle on living shoreline created marshes behind rock sill structures, but that most recruits are likely not surviving. Sediment organic matter (OM) and plant density were correlated with mussel abundance, and sediment OM increased with marsh age, suggesting that living shoreline design (e.g., sand fill, planting grids) and lags in ecosystem development (sediment properties) are reducing the survival of the young recruits. We offer potential modifications to living shoreline design and implementation practices that may facilitate self‐sustaining ribbed mussel populations in these restored habitats.

Highlights

  • The potential for natural infrastructure to protect coasts by slowing erosion and reducing storm surge and flooding can be considerable in many settings, in areas subject to high relative rates of sea level rise and vulnerability to storms (Arkema et al 2013, Sutton-Grier et al 2015, Narayan et al 2016)

  • The successful creation of a salt marsh ecosystem may be discernible by key components, including native marsh biota from several principal faunal groups including intertidal bivalves (Geukensia spp.), marine crabs (Uca spp., Callinectes spp.), marine snails (Littorina spp.), marsh fish (Fundulus spp.), estuarine turtles (Malaclemys terrapin), and marsh birds (e.g., Ammodramus caudacutus saltmarsh sparrow); species assessments can be used as performance indicators for marsh restoration efforts

  • Juvenile mussels were found in very low densities, when present, in living shoreline marshes (1.1 Æ 0.5 mussels/m2) compared with reference marshes (23.0 Æ 6.8 mussels/m2, t(12) = À3.146, P = 0.008)

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Summary

Introduction

The potential for natural infrastructure to protect coasts by slowing erosion and reducing storm surge and flooding can be considerable in many settings, in areas subject to high relative rates of sea level rise and vulnerability to storms (Arkema et al 2013, Sutton-Grier et al 2015, Narayan et al 2016). When used for shore protection, these created features (living shorelines ) often involve a combination of green-gray (hybrid) infrastructure, restoring or creating a fringing marsh in combination with a stabilizing sill structure placed offshore and parallel to the marsh (Bilkovic et al 2017a), which can be very effective at erosion protection (Shepard et al 2011, Gittman et al 2014, Morris et al 2019, Fig. 1) and more resilient than armoring (e.g., bulkheads) to storm events and sea level rise (Gittman et al 2014, Smith et al 2017, Mitchell and Bilkovic 2019). The successful creation of a salt marsh ecosystem may be discernible by key components, including native marsh biota from several principal faunal groups including intertidal bivalves (Geukensia spp.), marine crabs (Uca spp., Callinectes spp.), marine snails (Littorina spp.), marsh fish (Fundulus spp.), estuarine turtles (Malaclemys terrapin), and marsh birds (e.g., Ammodramus caudacutus saltmarsh sparrow); species assessments can be used as performance indicators for marsh restoration efforts

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