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APPENDIX C
Beneficial Use Options
Before deciding amongst beneficial
uses it is important to first determine whether the dredged material
is acceptable for beneficial use. Evaluation of the contaminant
status of the dredged material is the first step. In general,
contaminated sediments will not be suitable for a majority of
beneficial use applications. Thus, different applications may
require decontamination or treatment prior to use. Other things
to take into account are technical feasibility, environmental
acceptability, physical alterations, costs/benefits, and legal
constraints.
The distance of the proposed site from
dredging project site, accessibility, mode of transport, rehandling
requirements, and timing of the beneficial use need in relation
to the dredging needs are things that need to be considered when
evaluating the technical feasibility of a beneficial use application.
The use of dredged material in beneficial
use applications must first consider all applicable legal constraints,
including, but not limited to: state, county and local land use
zoning laws; ownership of disposal sites; national, state and
local regulations and standards.
Potential beneficial uses must take
into account any compelling environmental considerations on a
site-specific basis. Consideration must also be given to likely
interference with other uses at or adjacent to the site. For
instance, the creation of berms must avoid interference with
other uses such as fisheries, ports, harbors, outfalls and intakes.
The cleanliness of the sediment must also be considered due to
the different degrees of contamination that would/would not be
acceptable for some of the uses.
It is important for the physical, chemical
and engineering characteristics of dredged material to be identified,
including an examination of contaminants, prior to application
to a beneficial use. These characteristics will largely determine
which beneficial uses the specific dredged material is suitable
for. Ecological impacts of the discharge of dredged material
must also be taken into consideration.
Logistics must also be considered such
as site utilization, transport, handling, storage, and dewatering.
Categories of Beneficial
Use:
1. Land Improvement/Enhancement
a. replacement fill
E.g. - fill for abandoned/closed gravel
or clay mines
-fill for obsolete canals/docks
-strip mine reclamation: would require large quantities of dewatered
dredged material
b. capping
Dredged material is utilized as a cover
for contaminated dredged sediment disposed in open water or on
upland sites as a method of isolating the contaminated material
from the surrounding environment.
E.g. - Brownfield remediation
c. land improvement
Dredged material can be used to improve
the quality of land where the current land is not adequate to
support a planned use or where the elevation is too low to prevent
flooding.
d. Topsoil
Maintenance dredging produces sediment
mixtures of sand, silt, clay and organic matter that can be excellent
topsoil for use on agriculture fields.
e. Agriculture, Horticulture, Forestry
i. Agriculture: Livestock pastures
requiring natural grass colonization; incorporation of dredged
materials into marginal soils to provide additional nutrients
Considerations - heavy metal uptake by plants; salinity; oil
and grease; nutrient availability; pH; water content
ii. Horticulture: Production of crops of vegetables, fruits,
nuts, commercially grown plants, sod farms
iii. Forestry: used for improving marginal soil on timber
land; dredged material can have higher contaminant levels than
required for food production
f. Parks and Recreation
Include such developments as riverside/coastal
picnic areas, water parks, marinas, athletic fields, golf courses,
campgrounds, trails, and playgrounds
2. Shore Protection
a. beach nourishment
May be necessary along eroding beaches
to protect the historic profile of the beach and to moderate
the wave climate along the shoreline. Must also take into account
the effects of dredged material placement on beach organisms.
The dredged sediment used to nourish the beach must closely match
the sediment composition of the eroding beach and be low in pollutants.
Concerns to keep in mind when considering
this option include:
- impacts on benthic organisms
- impacts on offshore organisms
- impacts of dredge anchors and pipelines on environmentally
sensitive habitats (e.g. seagrass beds, dunes)
b. in-water disposal
In-water disposal of dredged material
is a beneficial use of the material. In recent years scientists
have noted that the net sediment transport of the Columbia River
has decreased. As a result, the beaches along the shores are
not receiving the quantities of sand that they once did and erosion
is threatening them. In-water disposal keeps the sand within
the littoral system and helps feed the beaches.
c. berm creation
Berms are used to improve beach stability
by modifying the shoreline wave climate. The berm may be designed
to alter wave direction and to modify the rate/direction of local
sediment transport. Could simultaneously be used for stockpiling
sand for beach nourishment purposes
3. Habitat Enhancement
Habitat enhancement is attractive as a low-cost mitigation procedure
that can be used to offset any environmental impacts that were
incurred during disposal. Restoration or enhancement is preferable
to habitat development.
Some environmental concerns related
to these activities include the loss of open water habitat, loss
of wetland systems, changes in the hydraulic and energy regimes
and potential pollutant mobilization by plants growing on contaminated
sediments.
Site selection should be based on knowledge
of the ecological characteristics of the site. Including, but
not limited to, foundation characteristics, salinity, tidal influences,
bottom topography, benthic communities, adjacent habitat, and
energy conditions.
a. Wildlife / Upland
Habitat development uses dredged material
as a substrate in the establishment and management of relatively
permanent and biologically productive plant and animal habitats.
Creation of wildlife islands for colonial nesting waterbirds.
Potential for creation/enhancement
of a variety of terrestrial communities ranging from dense forest
to bare soil.
Disadvantages to this form of beneficial
use include the possible need for long term management of the
site, limitations on future land use at the site, costs associated
with the rehandling of the sediment, management and control of
resulting effluent to ensure it meets water quality standards
Factors to consider during site selection
include: availability, capacity of disposal need, dredging area
proximity, physical and engineering characteristics, environmental
suitability, public acceptability, tidal considerations, and
habitat development feasibility.
b. Island
Primarily for migratory colonial nesting
waterbirds (e.g. Caspian terns, pelicans, cormorants, herons,
egrets etc). Confined disposal facilities (generally designed
for the permanent containment of contaminated sediments) may
also be useful for such habitat
Additional sediment can be added to
the island during the fall or winter when the birds are not there.
These islands tend to be attractive
to nesting waterbirds because they offer isolation from ground
predators and human disturbance; they have the ability to provide
a wide range of habitat diversity to accommodate the nesting
birds (e.g. bare ground, sparse cover, dense cover, and tall
shrubs and trees); ongoing dredging operations can keep this
type of successional habitat available.
c. Fisheries
Bottom mounding may improve fish habitat
when combined with stabilization techniques such as planting
seagrasses or capping with shell.
Creation of salt marshes for fishery
organisms.
d. Wetland restoration
The are different ways in which dredged
material can be used in the restoration of wetlands. Dredged
sediment could be applied in thin layers to bring degraded wetlands
up to an intertidal elevation. Wind and wave barriers may be
created to allow the regrowth of native vegetation and to prevent
erosion.
Potential problems with wetland restoration/creation
are:
- project timing: coordination of biological and dredging schedules
- bioaccumulation: contaminant uptake by plants
- invasion of non-native plant species
e. Aquatic
The establishment of biological communities
on dredged material at or below mean tide in coastal areas or
in permanent waters in lakes and rivers. These include tidal
flats, seagrass meadows, clam flats, oyster beds, fishing reefs,
and freshwater aquatic plant establishment. Aquatic habitats
have the potential to be highly productive biological units.
In many cases, it may be feasible to include aquatic habitat
establishment/enhancement as part of a wetland restoration project.
A major disadvantage, to date, is the lack of knowledge concerning
the techniques for the establishment of such biological communities.
4. Other
a. Construction products
Dredged material can be used in the
creation of the following products: concrete aggregates, backfill,
bituminous mixtures and mortar, bricks, ceramics, and insulation
pellets. It may also be used as riprap/blocks for the protection
of levees and slopes against erosion and for use on public roads
for snow and ice.
b. aquaculture
Dredged material containment areas
commonly possess structural features that enhance their suitability
as aquaculture areas. These features include levees and water
control devices. For instance, levees that would be constructed
or that currently exist to contain dredged material could also
serve to impound the water necessary for aquaculture.
Aquaculture has the potential to for
production of low-cost protein, contributing to demand for seafood,
increasing employment in supporting industries.
c. Industrial/Commercial Development
Port enhancement or expansion
d. Residential and Urban use
Use for fill, erosion control, foundation
material
e. Airports
Runways and facilities
f. Roads
Foundation material for highway/road
construction
Table C-1: Examples of beneficial
uses in the Columbia River (& other sites)
|
Project/Site Name |
Beneficial Use |
|
Columbia River Shoreline |
Beach Nourishment |
|
Columbia River |
Shoreline Stabilization |
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Columbia River levees |
Flood Control |
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Coos Bay berms |
Clam bed development |
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Miller Sands |
Wetland/Habitat development |
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Skamokawa Vista Park, WA |
sold for construction uses |
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Benson Beach, WA |
Beach nourishment |
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