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What is a wetland?
land that is saturated with water, either permanently or seasonally, such that it takes on the characteristics of a distinct ecosystem
Cowardin wetland definition
Lands transitional between terrestrial and aquatic systems where the water table is usually at or near surface or the land is covered by shallow water.
What is riverine?
‘related to or situated on a river or riverbank; riparian
Three part evaluation standard is
Vegetation (hydrophytes), soil (undrained hydric soil), hydrology (water during growing season)
Marine and Estuarine sytstems
mean low low water
Riverine and lacustrine =
2 m below low water
Cowardin classifications systems
Marine, estuarine, riverine, lacustrine, palustrine
Marine
saline > 30 ppt, go from continental shelf to open ocean terrestrial shores
Estuarine
mixed salinity down to 0.5 ppt, lying within enclosure of river, bays, and sounds up to terrestrial uplands
Riverine
< 0.5 ppt, lying within channel banks, usually has some flowing water
Lacustrine
< 0.5 ppt, lying within topographic depression or dammed channel, not more than 30% cover of vegetation, must be > 8 ha in size
Palustrine
< 0.5 ppt areas with vegetation, but tidal; also includes non-vegetated areas with no active shorelines, water depth must be < 2 m, and area must be < 8 ha; typically used to include anything that does not fit in the other systems
The value of wetlands?
habitat for migratory birds, 95% fish use marshes, richest carbon stores
Why are we losing wetlands?
Dredge and fill, development, agriculture, Channelization, diking, damming, alteration of hydrological flow Shoreline protection, removal of vegetation, mowing, grooming, Dropping/raising water level in soil, Relative sea level rise
Rivers and Harbors Act 1899
First major US environmental law; no dumping or unauthorized alteration of “navigable waters” – regulated by United States Army Corps of Engineers
Clean Water Act - Section 404
Can not dredge or fill a wetland. Need permit. No net loss of wetlands - lose an acre build an acre - mitigation
US vs. Riverside Bayview Homes
Adjacent wetlands included, with some hydrological connection to navigable waters
Rapanos vs. United States
Isolated wetlands not included, must have a “significant nexus” to navigable water; actually a split decision, no definite guidance for regulations to USACE
Sackett vs. EPA
Limited definition of jurisdictional wetlands to those with continuous connection to navigable water; intermittent connections not included
The three types of wetland laws?
1. Statutory law (US Congress, e.g. CWA)
2. Regulatory law (federal agency, published in the Federal Register, e.g. major procedures to implement statutory law)
3. Administrative law (rules created within federal agency, e.g. published manuals)
The USACE permit system is
a way to achieve ‘no net loss’ objective of Section 404
regulated by USACE
sets up compensatory mitigation req
Preference of permit system
1 avoid 2 minimize 3 mitigate
Types of mitigation
-Off-site mitigation or on-site
-Simple or in-advance mitigation banking
-Self banking or using In-Lieu Fee (ILF) program
Mitigation Banking
organized buying and selling of wetland restoration/conservation credits
the organized buying and selling of liability and responsibility to maintain wetland function into the future
-ILF mitigation banks are now the preferred option
Benefits of mitigation banking
The wetlands are replaced/constructed by a company that is in the business of restoration
When mitigation banking you have to consider
-Proximity of restoration to altered site is important
-Type of restoration is important (In-kind vs. Out-of-kind)
-Mitigation ratio: 1:1? 1:20? Are constructed wetlands as good
as natural wetlands? What are the rules for banking?
Wetland deliniation definition
defining the boundaries of a wetland, for compensatory mitigation
What is a “jurisdictional wetland” by USACE standards?
An area that exhibits hydrophytic vegetation, hydric soils, and wetland hydrology
HGM hydrogeomorphic method is better because
it allows wetlands to be compared based on functional equivalence
HGM steps
A. Classify the wetland
B. Find a reference site wetland, to use as a target
C. Identify the functional indices that will be used
D. Assess them
Reference site
a location or piece of land that is used as a benchmark to gauge the desired outcome of your restoration project, a model
Monitoring
Measuring and assessing the restoration project as it progresses over time
Types of monitoring
-pre-construction monitoring
-post-construction monitoring
-major grousing that it is an afterthought
Wetland hydrology
inundated either permanently, or semi-permanently and the soil is saturated at some time during the growing season of the prevalent vegetation
The key hydrological feature
- water has an overriding influence on soils and vegetation due to anaerobic and reducing soil
indicators of wetland hydrology
Stream or tidal gauge
Inundation or soil saturation
Watermarks
Driftlines - water floats junk far out
Sediment deposits
Drainage patterns
Crab holes/crawfish
3 hydrologic pathways to get water to your wetland
Groundwater-surface flow- precipitation
much of texas is -
surface flow
How can you manage hydrology
put water in and take it out
Hydrological Management Example:
Pterocarpus swamp forest in Humacao, Puerto Rico Problem: Pterocarpus forest dying due to salinity (canal opening and sea level rise), and lack of freshwater inflow (diking and draining)
-sugar cane plantations - land recovers - plantations abandoned and now lagoons - channel to drain water = turned to mangrove
Hydrological management:
1. Upstream inflow
2. Canals and diversions
3. Dikes and levees
4. Draining
5. Weirs
6. Subaqueous barriers
Hydrological Restoration:
removal or modification of anthropogenic barriers to flow; typically, a very cost- efficient method
Hydric soil
formed while saturated, flooded, or ponded during the growing season, with anaerobic microbial activity that depletes oxygen, causing reduced conditions
How does reduction happen?
Water saturation results in anoxia (no oxygen)
Anaerobic microbes that live in anoxic conditions generate their energy through a different metabolic pathway (fermentation) than aerobic microbes.
This pathway turns Fe3+ into Fe2+, and then Mn4+ to Mn2+, and finally S042- to H2S
Reduction refers to low soil redox potential, or reduction-oxidation potential (measured in mV)
Reduction increases plant stress by making it more difficult to acquire nutrients
indicators of hydric soil
Organic matter accumulation
Sulfur smell
Gleyed layers
Mottling or streaking
Concretions - small iron or magnesium masses, often generally spherical
A big problem for the restoration of wetland function:
good soil takes a long time to form. ~20-50 years to reach relatively similar carbon densities in the root zone (say around 15 cm of depth). ~1000 years or more to really be the same in the full profile.
So, how to restore and manage wetland sediments?
1. Promote vertical accretion at your site - Organic and autochthonous (by increasing plant productivity)
2. Promote (or inhibit) mineral sediment deposition by taking advantage of currents and transport patterns horizontally or from upstream
3. Get and move sediment for free when you can! - Beneficial Use’ of dredge spoil.
4. Follow the law and be a good neighbor when managing sediments – if dredging or digging, contain your sediment spoil with a boom and curtain – and, use sediment fencing or temporary diking to avoid runoff into the watershed or terrestrial areas
5. Protect the shoreline if there is wave or current erosion -Get the soil type as cohesive as possible
If the energy is substantial, protect using a living shoreline
(reef balls, shells, rock, shingle/old roots, geotubes, hard structures if needed)
Don’t worry about the vegetation for wave erosion
worry about the soils
Hydrophytic vegetation:
prevalent vegetation is composed of macrophytes that are adapted to inundation or saturation and thus anaerobic soil conditions
indicators of hydrophytic vegetation
A. Plant species
B. Morphological, physiological, or reproductive adaptations
A. Plant species
-more than 50% of dominant species are OBL, FACW, or FAC -Obligate (OBL), almost always in wetlands, > 99% of time -Facultative Wetland (FACW), usually in wetlands, > 67% of time -Facultative (FAC), about equal probability of being in wetland or not -Facultative Upland (FACU), < 33% of time in wetlands -Obligate Upland (UPL), <1% of time in wetlands
B. Morphological, physiological, or reproductive adaptations
pneumataphores
buttressed trunks
shallow or adventitious roots
floating leaves
floating seeds
how to restore and manage wetland vegetation?
1. Select your target vegetation mix -often primarily based on elevation relative to water level or water table -wetland vegetation communities are typically strongly zonated based on the hydrology
2. Decide whether to plant in an organized pattern or allow ‘self-organization’ to happen? –usually a combo is used
3. Draw up the planting plan (density and locations)
4. Buy the seed or transplants, or propagate them yourself from cuttings or rhizomes -most wetland plants work using cuttings/rhizomes, don’t even need rooting agent
5. Irrigate or fertilize -these are rarely-used for wetlands
6. Remove/manage invasive species -mechanical -chemical -fire -flood them out, etc
Integrated Solutions
biostabilization of rivers/shoreline banks
ecosystems as barriers to energy
ecosystems to ‘engineer’ the geomorphology of landscapes
integration of green and civil construction materials science
The key to shorelines that are ‘alive’ is not the structures, but rather
the ecological processes