Estuaries and Salt Marshes
An estuary is that area where the mouth
of a river meets the sea. Sea water mixes with
fresh river water to
form brackish water. It is
characterized by tides, by opposing
currents flowing outward from the river
and inward from the sea, and by
brackish water, which is a mixture of
sea and river water. Since salt water is
denser than fresh water, in an estuary,
incoming sea water forms a wedge
under the lighter river water. Mixing
occurs in the narrow zone between the
layers. Percent salt content (salinity) of an
estuary is less than that of sea water but
more than that of fresh water, and
changes every 12 hours with the tidal
cycle.
Another characteristic of an estuary is
the presence of sediment. River water
contains fine mud and silt that has
been washed off the land. As the river
widens into the estuary and meets the
sea water, the current slows and the
particles suspended in the water settle
to the bottom. The saline conditions in
the estuary also cause mud and silt to
settle; especially where fresh and salt
water mix. In the area of the estuary
closest to the ocean, mud and silt
deposits can form extensive mudflats
and sand banks (deltas).
River runoff also carries organic and
mineral matter which settle with the
estuary sediment (nutrient trapping).
This enriched sediment provides an
important source of nutrients for
microscopic one-cell animals (protozoans),
which are consumed by larger organisms in the
estuarine and
surrounding salt marsh food chains.
Decaying vegetation (microbial
biomass) in the salt marshes provides
an additional food source. Salt marshes
are common in estuaries often forming
on mudflats, and in the low coastal land
of sheltered bays and inlets.
What Animals and Plants Live in
Estuaries and Salt Marshes?
Confined to small, transitional areas
between the land and sea, estuaries
and salt marshes may support fewer
animal and plant species than do
marine or freshwater ecosystems, but
they still provide productive habitats for
many fish, shellfish and water birds.
A habitat is the natural home of a
plant or animal. Changes to this home
can affect the organisms that live
there, sometimes, in harmful ways.
Commercially important fish such as
flounder, salmon, trout, striped bass,
shad, gaspereau and smelt feed in
estuaries and migrate through them to
reach spawning grounds. Many birds
feed and over-winter in estuaries. The
nutrient-rich mudflats provide
abundant food for certain species of
shellfish including soft-shell clams,
mussels, periwinkles, crabs and
shrimp. Productive shellfisheries
are often found in estuaries.
Saltmarsh plants grow on mudflats that
have accumulated to a height where
they are exposed at low tide and
submerged at high tide. Salt-tolerant
plants (halophytes) such as cordgrasses
(spartinas), are common in salt
marshes and can withstand periodic
submergence and waterlogged soil. In
the Bay of Fundy, spartinas provided
salt hay for early settlers.
How are Estuaries and Salt
Marshes Disrupted?
Estuaries and salt marshes can be
disrupted by events occurring in the
river, the sea or the estuary itself.
These disruptions can also affect
nearby coastal areas that are
dependent on the estuarine ecology.
Natural events can be disruptive.
Storms and floods, from tidal surges or
from the river, can erode mudflats and
the seaward edge of salt marshes.
Whereas salt water flooding can kill
terrestrial plants and extend the marsh
area. Flooding by fresh water can
damage the marsh and erode channels.
Ice buildup can scour mudflats. A thick
blanket of ice can deprive surface-
dwelling organisms of much needed
oxygen.
Salt marshes are common
in estuaries often forming
on mudflats and in the
low coastal land of
sheltered bays and inlets.
Human activity can cause severe
disruptions to estuaries and salt marsh
habitats. Many cities and towns have
been built around estuaries, which offer
natural transport and shipping lanes.
Saltmarsh land is flat and easy to build
upon when drained or filled. Developed
areas continue to be disrupted through
dredging, dumping of dredge material,
shipping and other port activities,
development of recreational facilities and
overharvesting of fish and shellfish.
Estuaries may also be affected by
industrial or urban development occurring
upriver, by drainage projects, flood
control activities and agricultural runoff.
Estuaries and salt marshes can be disrupted
by natural events, such as storms and floods.
Human activity, including urban development and
agriculture can cause severe and long-lasting
damage.
Pollution can affect an estuary in four
major ways: 1) oxygen depletion (e.g. from
sewage), 2) chemical accumulation (e.g.
toxic organic compounds, petroleum
products, heavy metals), spills (e.g. oil.
spills) and thermal pollution (e.g. heated
effluent from power plants). Just as
nutrients collect in estuarine mudflats
through nutrient trapping, many pollutants
can also collect in the sediment. Microbial
activity can decompose some pollutants,
such as sewage, but others, such as heavy
metals, are bio-accumulative.
Draining and Diking
The drainage of salt marshes for farmland
and other developmental purposes, or to
control flooding, was widespread in Nova
Scotia. Channels were usually cut in the
marshes to reduce the amount of surface
water at high tide, while dikes were built
around the perimeters of the drained land
to prevent water from entering the marsh
area. Harvesting salt marshes can reduce
the amount of decayed vegetation entering
the aquatic food chain, which, in turn, can
reduce the populations of fish and shellfish
in adjacent waters. About half of the
32,000 hectares (80,000 acres) of Nova
Scotia salt marshes have been diked.
Fortunately, most of this land is high-level
marsh, as in the Bay of Fundy, and is
rarely flooded. Farming these areas
probably has little effect on the marine food chain.
Many organisms that live in estuaries
are close to their physiological limits of
tolerance, making them sensitive to
extra stress, such as oxygen depletion or
chemical pollution. They have adapted
to changing salinities, soft sediments
and, muddy waters and may suffer if
these conditions are altered.
Single or short-duration events may
harm species or major portions of the
habitat, but the damage should
eventually correct itself. For example,
storms or a single oil spill may impact
severely at first, eroding or covering
mudflats and salt marshes. However;
if no other disruptions occur, animal
and plant communities should return to
previous populations. Recovery time
depends on such factors as direction
of the current, rates of sedimentation,
hydrocarbon breakdown, and
regeneration of the grasses. Migrating
and young animals will also move into
the area, hastening its recovery.
Long-term discharges of pollutants or
recurrent pollution will have long lasting
effects. Persistent chemicals, such as
PCBs or heavy metals, accumulate in
the food chain and are absorbed
directly by invertebrates feeding on
sedimentary deposits. If the sources of
chemical pollution are removed, clean
sediment may eventually bury the
polluted layer, thus removing it from
the food chain. However, the polluted
sediment could be re-exposed through
storms or dredging, for instance
When salt marshes are burned or
drained to convert them to farmland,
fish and shellfish populations in the
estuary and surrounding coastal
areas may be reduced, creating
difficulties for certain inshore
fisheries. Such disruptions can be
irreversible if corrective action is not
taken.
Urban and industrial development of
the areas adjacent to estuaries and
salt marshes may destroy entire plant
and animal communities. The
marshes and mudflats may even be
eliminated. Undeveloped salt
marshes; however, can coexist with
industrialized areas and enhance
communities.
How Can Disruptions Be Prevented?
Many disruptions to estuaries and salt
marshes result from industrial and
urban development, or from poor land
use practices in the watershed upriver.
These effects may be difficult to
correct, although treatment of urban
and industrial waste will reduce
pollution from developed areas. In the
watershed, reducing soil erosion, water
diversion and toxic chemical runoff will
help protect habitats downriver.
Care must be taken to avoid
resuspending toxic materials that
may be embedded in the sediment.
Dredging and dumping of dredge
spoil, for example, could dislodge
such dormant toxic compounds.
Estuaries and marshes affected by
isolated and short-term events, such as
storms, floods, oil spills or organic
enrichment, may recover rapidly.
Microbial activity in the sediment can
break-down oil or organic pollution,
provided the amount and duration of
the pollution does not overwhelm the
ecosystem. In fact, in the case of
polluted mud, microbiological processes
may be preferred to artificial cleanup
methods.
Marsh habitats can be protected by
legislation aimed at controlling
development and waste dumping.
Preventative or corrective action to
preserve estuaries and salt marshes
depends on changes in land use,
development and industrialization. Such
planning and development falls under
the jurisdiction or regulatory authorities
of several federal and Nova Scotia
government departments.
For more information on these
sensitive habitats and how to eliminate
disruptions to them, contact:
The Nova Scotia Department of Fisheries
P0. Box 700
Pictou, Nova Scotia BOK IHO
Tel: (902) 485-5056
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