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Creating Successful Wetlands
1. Creating Successful Freshwater Wetlands
Ynes S. Arocho
BIO 690: Qualifying Exam
M.S. Environmental Science
http://www.westcreek.org/preserve.html
2. Overview
Wetland Loss
Ecosystem Services
Wetland Policy
Wetland Mitigation
Mitigation Banks
Wetland Function
Wetland Plant Development
Wetland Soil Development
Salvaged Soils
Reference Wetlands
Restoration Costs
Urban Wetlands
West Creek Reservation
Conclusions
3. Wetland Loss
56% of US wetlands
(Dahl, 1991)
90% of Ohio wetlands
(Dahl, 1991)
Over half the world’s
wetlands are lost or
severely degraded (Yallop
and O’Connell, 2000)
Source:http://www.nwrc.usgs.gov/wdb/pub/others/wetstatus.pdf
4. Wetland Policy
Section 404 of the
Clean Water Act
Compensatory
mitigation
“No Net Loss”
Regulation has three
levels:
Avoidance
Minimization
Compensation
http://onlinelibrary.wiley.com/doi/10.1111/j.1474-919X.2004.00333.x/full
5. Wetland Mitigation
Four options
Establish a new site
Restore a previously
exiting site
Enhance function of
an existing site
Preserve an existing
site
Mitigation ratio
Type and size of
wetland destroyed
determines type and
size of created
wetland required.
Required ≠ Actual
6. National Research Council Study, 2001
Purpose: evaluate
wetland mitigation
practice.
Plant species
composition = 10 or
more yrs to stabilize
Soil development = 3-
30 yrs to stabilize
Plant assemblages
do not replace
function
Recommendation:
Both plant community
structure and wetland
function should be
considered during
mitigation.
Resulting wetland
should be self-
sustaining
− Wetland hydrology
7. Mitigated Wetlands in Ohio
Kettlewell,2005
101 mitigation sites
425.3 acres impacted
697.8 acres required
496.8 acres actual
(71.2% of required)
Mitigation ratio 1.17:1
1.17 acre created / 1
acre destroyed http://www.ohiodnr.com/Home/wild_resourcessubhomepage/Researcha
ndSurveys/WildlifePopulationStatusLandingPage/WoodDuck/tabid/1933
4/Default.aspx
8. Compliance Performance Standards
Vary among permits
Vary among similar
wetland types
Some too stringent or
too modest
Difficult to determine
success or failure
Examples: minimum
# native plants,
survival of # woody
species
http://andreawilliamsministries.com/what-does-success-really-mean-
anyways/success-and-failure-road-sign-with-dramatic-clouds-and-sky/
9. Mitigated Wetlands in Illinois
Matthews and
Endress, 2008
76 mitigation sites
113.6 hectares
proposed
31.7 hectares deficit
Applied performance
standards
8 failed all goals
45 met some goals
23 met all goals
Matthews and Endress, 2008
10. Mitigation Banks
Large wetland area
Sell mitigation credits
(hectares of
wetlands) to parties
required to mitigate.
2005 estimates:
363 active banks
75 sold out banks
169 proposed banks
78% are for-profit
http://www.dot.state.oh.us/DIVISIONS/TRANSSYSDEV/ENVI
RONMENT/ECOLOGICAL_RESOURCES_PERMITS/MITIGA
TIONINVENTORY/Pages/default.aspx
ODOT Mitigation
Inventory
11. Wetland Function
Federal standards
measure vegetation for 5
yrs.
Do not measure:
Biotic integrity
Nutrient cycling
Trophic dynamics
Hydrology
Soils
Fauna
Microbial characteristics
Recommendation:
Mitsch and Wilson, 1996 and
Zedler, 2004
Require longer
monitoring periods
Plant characteristics
alone are not
adequate
measurements of
wetland function
12. Wetland Plant Development
Mitsch et al. 2005
Planted vs. unplanted
Vegetation cover vs.
plant diversity
Pulsing experiment:
Planted wetland: plant
cover from 73% to
62%.
Unplanted wetland:
plant cover from 74%
to 38%.
Mitsch et al., 2005
13. Wetland Soil Development
Mitsch et al. 2005
Prior to creation: no
hydric wetland soils
2 yrs later:
78% of samples
(0-8 cm)
24% of samples
(9-16 cm)
10 yrs later: 94% of
samples in both layers.
Supports NRC, 2001
Mitsch et al., 2005
14. Salvaged Soils
McKinstry and
Anderson, 2005
Soil from donor wetland
used to create new
wetland
Increased plant
composition compared
to control group
Combination of
salvaged soils and
plantings?
http://www.pacificexc.com/projects/main.php?g2_itemId=468
15. Reference Wetlands
Campbell et al., 2002
Compared soils and
plants
Soil chroma, defines
soils; low = wetland; high
= upland
Higher in created sites
Plant species richness
lower in created sites.
Higher percent of upland
plant species in created
sites.
Stolt et. al., 2000
Compared wetland
topography
Created sites: 40-60%
less elevation change
across area
Created sites: very little
microrelief
Provides habitat variety
thus increasing
biodiversity
16. Restoration Costs
Gutrich and Hitzhusen, 2004
Ecological-economic
computer simulation model
Functional indicators: plant
species richness, hydric soils
and native plants
Prediction: 7-44 yrs to reach
functional equivalency
Prediction: $5190-$309,108
lag cost above private cost
Recommendations:
1) Require a bond equal to
estimated benefits provided
by wetland – high restoration
cost with low lag cost vs. low
restoration cost with high lag
cost
2) Delay issuance of drainage
permit until functional
equivalence is achieved in
replacement – no lag costs
3) Use wetland banks –
functional equivalency already
established
17. Urban Wetlands
Obstacles: hydrology,
habitat, infrastructure,
pests and people
Goal: rehabilitation not
restoration to their original
condition
Difficult to evaluate
success: criteria must
reflect ecology of wetland
with reality of urban
context.
Source:http://www.biohabitats.com/ndg_newsite/newsletter/2010spring/article.urbecrest.php
18. Urban Wetland Assessment
Correct use of
reference wetland
Undisturbed site
Degraded sites
Success: restored site
more similar to
undisturbed reference
site without similar
response in the
degraded control site.
Grayson, et al., 1999 http://office.microsoft.com/en-us/images/results.aspx?
qu=grades#mt:0
20. West Creek Reservation
West Creek Preservation
Committee (citizen goup)
Part of Cleveland
Metroparks System
Parma, Seven Hills,
Brooklyn Heights and
Independence
Highly urbanized area
Tributary to Cuyahoga
River
http://www.westcreek.org/preserve.html
21. West Creek Wetlands
Old municipal landfill
Created and planted
in 2002
Wetland design (step-
down wetlands)
Plant surveys –
increased range
Usage: recreational,
educational and
habitat for animals.
Source: www.maps.google.com
Photo by: Ynes Arocho
23. Conclusions
Progress so far:
Replace function
Salvage soils
Plantings
Hydrology
Mitigation banks
Ecosystem
services
Ideas for the future:
Reevaluate policy
Standardize
permit
requirements
Encourage use of
mitigations banks
Further research
on function
Further explore
valuing services