Freshwater Wetland Restoration
I. Types
of systems, based upon hydrology:
Riparian
Water level: High
variation
Water supply: Dependable
Characteristic vegetation: fast growing, disturbance associated
Water level: Cycling, dries out or dries down every year
Water supply: Variable; years of high supply and low supply
Characteristic vegetation: annuals, endemics
Constant water level
Beaver ponds, ground-water fed, lacustrine, low ET environments, montane
Water level: narrow range
Water supply: constant
Characteristic vegetation: emergents, aquatics
High fluctuation
Stormwater-associated, or natural drainage ponds in arid
environments
Water level: may vary across season or fluctuate with each precipitation event.
Water supply: highly variable
Characteristic vegetation: weedy species, disturbance opportunists
Oligotrophic
Fens, bogs, peatlands
Water level: may be constant or quite variable; some bogs get quite dry
Water supply: dependable
Water quality: low nutrient; minimal
contact with mineral soil
Characteristic vegetation: Slow
growing, stress-tolerators, nutrient-intolerant
systems, acid-loving, sedge or sphagnum dominated, dwarfed
Saturated soils
Areas adjacent to wetlands, streams and lakes often have
continually saturated
soils. Wet meadows, pastures and
prairies may also be saturated much of the
Water level: low but constant; soil saturated for much of growing season.
Water supply: constant
Characteristic vegetation: because of grazing, many areas of saturated soils are
highly susceptible to invasive species, esp. grasses like reed canarygrass.
II. Functions, and how you get your wetland to
perform them.
Functions that are commonly attributed to wetland
ecosystems
Water quality improvement
-sediment removal
-nutrient removal
Hydrology
-flood flow attenuation
-recharge
-bank stabilization and erosion control
Habitat
-specific habitat types
-primary productivity
How is each function generated in a restoration
project?
Vegetation
Shaping the land
Modifying or
controlling hydrology
Using landscape
ecology
Engineering
Location
Organic material
Structures
Sediment removal
Wetland or stream
-Accomplished by slowing down flowing water
Vegetation
Increased cross-section
Increased sinuosity of stream path
Increased residence time
Nutrient removal
Wetland or stream
-
Denitrification
-
Flushing or leaching of nitrates
-
Nitrogen uptake
-
Phosphorus removal requires soil contact
Flood-flow attenuation
Wetlands and streams
-
Sinuosity
-
Vegetation (woody best)
-
Constrictions
-
Bottom friction (many shallow channels)
-
Storage capacity
Recharge
Wetland
In a
wetland, you need
-A
permeable layer
-Water source
-Adequate head
Bank stabilization and erosion control
Wetland
Fast-growing, energy absorbing woody vegetation good
In
coastal wetlands, stabilization is achieved by
- Energy-absorbing vegetation
- Shallow water (frictional dissipation of energy)
- Minimal fetch
Primary production
Wetlands and streams
Production encouraged by growth of vegetation along streams and by
contributions of detritus to aquatic systems.
- Shallow shorelines with sunlight are very productive
- Many aquatic systems are very leaky and have flow-through of detritus,
nutrients, water
Habitat
Wetland
Wetland
types are many, but you usually have little choice as to type
Wetlands often differ in plant composition from site to site
- So multiple wetlands can increase diversity
Maximize shallow-water area
Minimize open water
Constructed habitat features also common
Streams
Pool/riffle ratios
In-stream wood
Overhanging vegetation
In-stream shelters
Side
channels
III. Problems
encountered in the restoration of each wetland hydrologic type
Riparian
Wetlands associated with riparian systems often depend
on river flooding for
recharge. The return interval of
flooding may be variable. Flood
control
practices often minimize minor flooding and result in catastrophic floods.
Floodplains may have spotty soils with areas of very
quick drainage and poor
nutrients.
High flood energy may cause disturbance, loss of
biomass.
Compromised buffers.
Water level: High
variation
Water supply: Dependable, but at varying intervals
Characteristic vegetation: fast growing, disturbance associated
Vernal
Vernal systems, because they dry out, have often been
drained and plowed, and
are regularly grazed. Grazing is
often associated with an increase in invasive
plant species in vernal ponds. Endemism
is high in vernal ponds, so restoration
efforts must observe guidelines that protect the genetic integrity of such
systems. Because they often cascade across the landscape, they may cross
property lines; restoration in multiple ownerships is difficult.
Water level: Cycling, dries out or dries down every
year
Water supply: Variable; years of high supply and low supply
Characteristic vegetation: annuals, endemics
Constant water level
Wetlands with constant water levels are susceptible to
changes in watersheds
caused by development, road construction, drainage projects, forest harvest,
beaver eradication, and a number of other factors that can alter the delivery of
water from a system or its retention in the wetland.
Systems that retain a constant water level are often very good candidates for
restoration, unless there is a particular weedy plant that thrives in a constant
water level. For instance, if the
site is highly disturbed, cattail may invade
and dominate the site.
Beaver ponds, ground-water fed, lacustrine, low ET
environments, montane
Water level: narrow range
Water supply: constant
Characteristic vegetation: emergents, aquatics
High fluctuation
High fluctuation systems can be very difficult to
restore, but can have a high
level of functional performance with a low level of species diversity.
Diversity tends to drop as water level variation increases (either depth or
frequency of variation).
Stormwater-associated, or natural drainage ponds in
arid environments
Water level: may vary across
Water supply: highly variable
Characteristic vegetation: weedy species, disturbance opportunists
Oligotrophic
Oligotrophic systems exist because of a disconnection
between mineral soil
(source of nutrients), and the water in the wetland.
These kinds of conditions
exist in fens and bogs, where peat has built the wetland up and separated it
from the soil, and in montane wetlands, where there is little weathered soil to
release nutrients. Most degradation
in oligotrophic systems happens when
nutrients are released into them. Watershed-level
modifications, most of them
difficult to reverse, are usually the main culprit.
Increased nutrients allow
invasive species to enter wetlands formed under low-nutrient conditions and
outcompete existing vegetation. Restoration
may involve fixing watershed
problems, or separating nutrient-rich water from the flow into the fen or bog.
Fens, bogs, peatlands
Water level: may be constant or quite variable; some bogs get quite dry
Water supply: dependable
Water quality: low nutrient; minimal
contact with mineral soil
Characteristic vegetation: Slow
growing, stress-tolerators, nutrient-intolerant
systems, acid-loving, sedge or sphagnum dominated, dwarfed
Saturated soils
Flat areas on flood plains may be intermittently flooded
or may have poor
drainage. Alluvial soils often make
them attractive for agricultural use,
particularly for grazing. Because
they are wet, have moderately fertile soils,
and often have a continuing history of disturbance and importation of non-native
plant species, such sites are often heavily invaded by quite persistent invasive
plants. Removal of such species is
difficult. In riparian areas,
conversion
back to riparian forest may be a sensible objective.
Areas adjacent to wetlands, streams and lakes often
have continually saturated
Wet meadows, pastures and prairies may also be saturated much of the
Water level: low but constant; soil saturated for much of growing season.
Water supply: constant
Characteristic vegetation: because of grazing, many areas of saturated soils are
highly susceptible to invasive species, esp. grasses like reed canarygrass.