Abstract

AbstractRibbed mussels (Geukensia demissa) are a highly abundant bivalve filter feeder throughout the salt marshes of the U.S. Atlantic Coast. These mussels form a mutualistic relationship with smooth cordgrass Spartina alterniflora wherein the grass provides habitat and shade to the mussels, and the mussels stabilize the sediment and fertilize the grass. Salt marshes are, however, rapidly changing and eroding as humans modify the coast, and the rate of sea level rise is accelerating. In order to understand how ribbed mussels may respond to their changing habitat, we collected mussel density and distribution data from 30 marshes covering the range of geomorphic settings found in lower Chesapeake Bay. We used a combination of in situ and GIS‐derived spatial variables to develop spatially applied models of ribbed mussel density and physical condition. Of the estimated 1.06 billion ribbed mussels in Virginia, we found that mussels were most abundant along the front edge of marshes in wide creeks, rivers, or bays with dense Spartina and minimal proximal forest, set in agriculturally dominated areas. In contrast, mussel condition was highest in fringing marshes located in narrow tidal creeks. Ribbed mussels responded to factors at a variety of scales, ranging from extremely local (0.5 m) to larger shorescapes (≥300 m). The methods that we used to create models linking both aquatic and terrestrial variables to explain the variation in ribbed mussel populations along the shoreline provide a valuable tool for identifying baselines and assessing potential for change across estuary‐level spatial scales not only for ribbed mussels in the Chesapeake Bay, but also for other sessile, intertidal species in other systems.

Highlights

  • Salt marshes are one of the major vegetated interfaces between land and water throughout the world’s temperate zones and are among the most productive ecosystems on the planet (Lieth 1972), providing a wealth of ecosystem functions and services including wave energy reduction and erosion control (Cooper 2005), nitrogen removal (Valiela and Teal 1979, Nelson and Zavaleta 2012), and habitat provisioning (Dıaz-Ferguson et al 2010, Angelini et al 2015, Valiela 2015)

  • Distribution and condition index We found that ribbed mussels were most abundant along the front edge of marshes in wide creeks, rivers, or bays with dense Spartina alterniflora and minimal proximal forest, set in agriculturally dominated areas

  • Throughout Virginia, approximately 30% of all marshes fall into the exposure regime typical of the high-mussel density platform marshes of this study

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Summary

Introduction

Salt marshes are one of the major vegetated interfaces between land and water throughout the world’s temperate zones and are among the most productive ecosystems on the planet (Lieth 1972), providing a wealth of ecosystem functions and services including wave energy reduction and erosion control (Cooper 2005), nitrogen removal (Valiela and Teal 1979, Nelson and Zavaleta 2012), and habitat provisioning (Dıaz-Ferguson et al 2010, Angelini et al 2015, Valiela 2015). Ribbed mussels are noted for being extremely efficient filter feeders (Galimany et al 2015). Their ability to improve water quality rivals that of oysters, and even exceeds oysters at the smallest particle sizes (Kreeger and Newell 2001). The fertilized Spartina increases its aboveground biomass, which facilitates increased sedimentation (Bertness 1984). This partnership between ribbed mussels and Spartina results in a more resilient marsh (Smith and Frey 1985)

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