NATIONAL
 ESTUARY
 PROGRAM
EFFECTS  OF  ARTIFICIAL  SHORELINES
Natural shorelines, including marshes and beaches, are critical for maintaining the ecological health of estuaries by stabilizing the shoreline, reducing
erosion, and providing critical habitat for commercially and ecologically important aquatic species. Over the past 30 years, Barnegat Bay has lost a greater
percentage of natural shoreline to coastal development than have other estuaries in the mid-Atlantic region. Specifically, 36% of the natural shoreline in
Barnegat Bay has been bulkheaded—replaced by watershed retaining barriers—representing a significant loss of natural habitat, particularly marshes and
estuarine beaches.
Bulkheads extend out from the original shoreline, altering the flow of water and the deposition of sediments, especially fine sand and silt. This often leads to decreased water clarity
and quality. Bulkheads also eliminate shallow aquatic habitats that are especially important as refuge areas for small organisms and the juveniles of large organisms. As a result,
the areas in front of bulkheads typically have a reduced abundance and diversity of organisms that live on the bottom and in the water column. In the United States, most research
on the effects of bulkheads has been done along the West Coast. There is little information on how bulkheads affect aquatic habitats or organisms in New Jersey estuaries.
THE NATIONAL ESTUARY PROGRAM IN ACTION
                                                                Barnegat Bay National Estuary Program
In the summer of 2006, with
funds from the Barnegat Bay Na-
tional Estuary Program, research
was conducted by Rider Univer-
sity  to compare the sediment
characteristics,  depth profiles,
species diversity, and abundance
offish and decapods (e.g., crabs
and shrimp) in front of bulkheads
and two types of natural  shore-
lines  (marsh  and beach)  in the
Little Egg Harbor portion  of
Barnegat Bay.
          In the  summer of 2007, the
          study was expanded throughout
          Barnegat Bay. Sampling site se-
          lection took into account the ex-
          tent of coastal development sur-
          rounding the sampling sites, and
          photographs from the 1920s and
          1950s were used to account for
          "bulkhead history" - the type of
          natural shoreline  the current
          bulkheads replaced. As a result,
          an equal number of bulkheads
          that  replaced  marshes  and
                                    beaches were sampled in each
                                    section of the Bay.

                                    Some important  physical char-
                                    acteristics of the habitats in front
                                    of bulkheads were very different
                                    from natural shoreline habitats.
                                    Sediment composition  differed
                                    among the shoreline types: bulk-
                                    heads contained more of the
                                    largest-sized  sediment than ei-
                                    ther beaches or marshes, and
                                    bulkhead shorelines contained
 EFFECTIVE
                   EFFICIENT
ADAPTIVE
COLLABORATIVE

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                     far  less  of the smallest-sized
                     sediment   than  did  marshes.
                     These  changes  in  sediment
                     characteristics  are  consistent
                     with more  turbulent water flow
                     in front of bulkheads as com-
                     pared to the natural shorelines.
                     They  influence the abundance
                     and diversity of bottom-dwelling
                     organisms  by  discouraging  or-
                     ganisms that bury in fine sedi-
                     ments or that prey on buried or-
ganisms from occupying habitats
in  front  of  bulkheads.  Faunal
communities  along  bulkheads
differed from those  of  natural
shorelines. In each section of the
estuary sampled, the total num-
ber of organisms such as fish,
crabs, and shrimp at the bulk-
heads was lower than at either
type  of  natural shoreline.  On
several occasions,  nothing was
caught  in front of  bulkheads.
Species diversity was also con-
sistently  lower in front of bulk-
heads. The composition of the
individuals captured  in front of
bulkheads suggests  that bulk-
heads are poor  refuge areas for
small prey species and the juve-
niles of larger predators. Several
small  prey species  that were
never  caught in front of bulk-
heads, including blueback her-
ring, killifishes,  menhaden, na-
ked  goby, striped mullet,  and
sheepshead minnow, were cap-
tured at the natural shorelines.
Habitats  in front of  bulkheads
are  significantly  deeper  than
those of natural shorelines, and
are characterized by larger indi-
viduals of both prey and preda-
tor  species. Individuals of five
prey species (alewife, anchovy,
silverside,  grass  shrimp,  and
sand shrimp) were captured at
all shoreline types. Individuals of
three of those species were sig-
nificantly larger in front of bulk-
heads  than  at  either  natural
shoreline.  Individuals  of  nine
predator  species  (black  drum,
bluefish,    northern    kingfish,
northern pufferfish, silver perch,
summer flounder, tautog, weak-
fish, and winter flounder)  were
captured at all shoreline types
and, on average,  individuals of
four of those species were sig-
nificantly larger in front of bulk-
heads  than  at  either  natural
shoreline.

These  findings  suggest   that
bulkhead habitats are not as bio-
logically rich as natural shoreline
habitats and may function differ-
ently. In addition, if current sea-
level-rise scenarios for the mid-
Atlantic are accurate, bulkheads
may accentuate the negative ef-
fects of sea-level rise on nursery
habitats in Barnegat Bay.

Visit www.bbnep.org to learn
more about this and other BBNEP
efforts.

EPA's National Estuary Program
(NEP) is a unique and successful
coastal watershed-based program
established in 1987 under  the
Clean  Water Act Amendments.
The  NEP involves the public and
collaborates with partners  to pro-
tect, restore, and maintain the wa-
ter quality and ecological integrity
of 28 estuaries of national signifi-
cance located in 18 coastal states
and Puerto Rico.

For more  information  about  the
NEP go to  www.epa.gov/owow/
estuaries.
The NEP:  Implementing the Clean Water Act in ways that are Effective, Efficient, Adaptive, and  Collaborative.
                                                                                        EPA-842F09001

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