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COMPENSATING FOR WETLAND LOSSES UNDER THE CLEAN WATER ACT
Appendix C
Analyses of Soil, Plant, and Animal Communities for Mitigation Sites Compared with Reference Sites
Trajectories for restoration in various mitigation studies are shown in comparison to conditions in reference marshes. The “>” and “<” signs mean that the equilibrium takes more time or less time, respectively, than the age of the mitigation site (years) when the survey was conducted or the data were modeled to project an age.
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COMPENSATING FOR WETLAND LOSSES UNDER THE CLEAN WATER ACT
TABLE C–1 Analysis of Soil, Plant, and Animal Communities for Mitigation Sites Compared with Reference Sites
Component
Location
Sites
Years
Source/Notes
1. Soils
California
1
>22, if ever
Zedler and Callaway (1999); salt marsh
Organic matter/% carbon
Louisiana
30
>20
Turner et al. (1994); backfilled marsh
North Carolina
7
>17
Sacco et al. (1994); planted salt marsh
Illinois
2
>7
Mitsch and Flanagan (1996); fresh marsh
Oregon
1
>5
Gwin et al. (1990); fresh marshes
Pennsylvania
44
?
Bishel-Machung et al. (1996); fresh marsh
Metanalysis
19
≫10
Streever (2000); coastal dredged sites
South Carolina
2
>3
LaSalle et al. (1991); salt marsh
Macroorganic concentration
North Carolina
1
>3
Moy and Levin (1991); planted salt marsh from uplands
North Carolina
5–7
>25
Craft et al. (1988); Craft (2000)
Carbon, nitrogen, and phosphorus concentration
California
1
40+
Zedler and Callaway (1999); salt marsh
North Carolina
5
>30
Craft et al. (1988); salt marsh
Illinois
2
>7
Mitsch and Flanagan (1996); fresh marsh
Exchangeable ions
South Carolina
2
>3
LaSalle et al. (1991); salt marsh
Grain size
North Carolina
1
>3
Moy and Levin (1991); planted salt marsh from uplands
Nutrient cycling
Texas
3
>17
Montagna (1993)
Sulfide and nitrogen
California
1
>15
Zedler (1990)
Average of six soil indices
California
4
>5
Zedler and Langis (1991); salt marsh
Nutrient exchange
North Carolina
1
>5
Craft et al. (1991); salt marsh
2. Plants—trees
Ohio
10
>50
Niswander and Mitsch (1995); riparian wetland, simulation model
Plant cover
Atlantic and Gulf
68
5–7
Matthews and Minello (1994); literature review
Louisiana
30
>20
Turner et al. (1994); backfilled marsh
Oregon
1
3
Frenkel and Morlan (1990); hay farm restoration
Height and biomass
California
4
>5
Zedler and Langis (1991); salt marsh
California
1
>11, if ever
Zedler and Callaway (1999); salt marsh
North Carolina
1
5
Broome et al. (1986)
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COMPENSATING FOR WETLAND LOSSES UNDER THE CLEAN WATER ACT
Species richness/cover
Connecticut
5
>10
Confer and Niering (1992); freshwater marshes
Illinois
2
>7
Mitsch and Flanagan (1996); fresh marsh
Native plant species
Portland, Oregon
51
>5
Magee et al. (1999); fresh marshes
Ratio above- to below-ground biomass
North Carolina
1
10
Broome et al. (1986)
Below-ground biomass
Texas
14
10
Shafer and Streever (2000); salt marsh
Three taxa
Metanalysis
12–14
>10
Streever (2000); coastal dredge sites
3. Fish and fisheries
Finfish number, biomass
California
1
>2
Chamberlain and Barnhart (1993); salt marsh
Finfish number
California
1
5
Zedler (1990)
Fish species number
Florida
21
10
Roberts (1991)
Fish and shrimp
North Carolina
Review
<3
Fonseca et al. (1990); sea grasses
Marsh resident fish biomass
North Carolina
3
>3
Minello (2000)
Marsh fisheries species
Texas
>6
Rulifson (1991); salt marsh
Biomass and number of finfish and shrimp
Florida
1
>2
Moy and Levin (1991); planted salt marsh from uplands
4. Marsh invertebrates
Marsh infauna number
North Carolina
1
>3
Moy and Levin (1991); planted salt marsh from re-graded uplands
California
4
>5
Zedler and Langis (1991); salt marsh
Marsh infauna biomass
North Carolina
1
2
Cammen (1976); salt marsh
Marsh infauna biomass
North Carolina
1
1
Cammen (1976); salt marsh
Marsh infauna biomass
North Carolina
7
>25
Craft (2000)
Marsh infauna species, and species proportions
North Carolina
7
<17
Sacco et al. (1994); planted salt marsh
California
4
>5
Zedler and Langis (1991); salt marsh
Marsh infauna species number and biomass
North Carolina
7
>17
Sacco et al. (1994); fresh marsh
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COMPENSATING FOR WETLAND LOSSES UNDER THE CLEAN WATER ACT
Component
Location
Sites
Years
Source/Notes
Marsh infauna biomass, and number
Florida
1
>2
Vose and Bell (1994); salt marsh impoundment
Larval dipterans
Florida
10
<11
Streever et al. (1996); fresh marsh
Macrobenthos
South Carolina
2
4–8
LaSalle et al. (1991); salt marsh
Epibenthos
Washington
1
>5
Simenstad and Thom (1996); salt marsh
Fish abundance
Metanalysis
11
5?
Streever (2000)
Total crustaceans abundance
Metanalysis
9
>12
Streever (2000)
5. Birds
Endangered species
California
1
>15
Zedler (1990)
Bird species number
Florida
21
<10
Roberts (1991)
Waterfowl
Iowa
30
<3
van Rees-Siewart and Dinsmore (1996); fresh marsh
Natural assemblages
Iowa
30
>5
van Rees-Siewart and Dinsmore (1996); fresh marsh
Portland, Oregon
51
>5
Magee et al. (1999); fresh marsh
Metanalysis
NA
?
Streever (2000); dredged marshes
Texas
7
>13
Melvin and Webb (1998); dredged marshes
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COMPENSATING FOR WETLAND LOSSES UNDER THE CLEAN WATER ACT
References
Bishel-Machung, L., R.P.Brooks, S.S.Yates, and K.L.Hoover. 1996. Soil properties of reference wetlands and wetland creation projects in Pennsylvania. Wetlands 16(4):532–541.
Broome, S.W., E.D.Seneca, and W.W.Woodhouse, Jr. 1986. Long-term growth and development of transplants of the salt-marsh grass Spartina alterniflora. Estuaries 9:63–74.
Cammen, L.M. 1976. Abundance and production of macroinvertebrates from natural and artificially established salt marshes in North Carolina. Amer. Midl. Nat. 96(2):487–493.
Chamberlain, R.H., and R.A.Barnhart. 1993. Early use by fish of a mitigation salt Marsh, Humbolt Bay, California Estuaries 16(4):769–783.
Confer, S.R., and W.A.Niering. 1992. Comparison of created and natural freshwater emergent wetlands in Connecticut (USA). Wetlands Ecol. Manage. 2(3):143–156.
Craft, C. 2000. Co-development of wetland soils and benthic invertebrate communities following salt marsh creation. Wetlands Ecol. Manage. 8(2/3):197–207.
Craft, C.B., S.W.Broome, and E.D.Seneca. 1988. Nitrogen, phosphorus and organic carbon pools in natural and transplanted marsh soils. Estuaries 11(4):272–289.
Craft, C.B., E.D.Seneca, and S.W.Broome. 1991. Porewater chemistry of natural and created marsh soils. J. Exp. Mar. Biol. Ecol. 152(2):187–200.
Fonseca, M.S., W.J.Kenworth, D.R.Colby, K.A.Rittmaster, and G.W.Thayer. 1990. Comparisons of fauna among natural and transplanted eelgrass Zostera marina meadows: criteria for mitigation. Mar. Ecol. Prog. Ser. 65(3):251–264.
Frenkel, R.W., and J.C.Morlan. 1990. Restoration of the Salmon River Salt Marshes: Retrospect and Prospect Corvallis, OR: Department of Geosciences, Oregon State University.
Gwin, S.E., M.E.Kentula, and E.M.Preston. 1990. Evaluating Design and Verifying Compliance of Wetlands Created Under Section 404 of the Clean Water Act in Oregon. EPA/ 600/3-90/061. Environmental Research Laboratory, Office of Research and Development, U.S. Environmental Protection Agency, Cornvallis, OR. 122 pp.
LaSalle, W.M., M.C.Landin, and J.G.Sims. 1991. Evaluation of the flora and fauna of Spartina alternifora marsh established on dredged material in Winhay Bay, South Carolina. Wetlands 11(2):191–208.
Magee, T.K., T.L.Ernst, M.E.Kentula, and K.A.Dwire 1999. Floristic comparison of freshwater wetlands in an urbanizing environment Wetlands 19(3):517–534.
Matthews, G.A., and T.J.Minello. 1994. Technology and Success in Restoration, Creation, and Enhancement of Spartina alterniflora Marshes in the United States. Vol. 2. Inventory and Human Resources Directory. NOAA Coastal Ocean Program Decision Analysis Series No. 2. Silver Spring, MD: U.S. Dept. Commerce, National Oceanic and Atmospheric Administration.
Melvin, S.L., and J.W.Webb. 1998. Differences in the avian communities of natural and created Spartina alterniflora salt marshes. Wetlands 18(1):59–69.
Minello, T.J. 2000. Temporal development of salt marsh value for nekton and epifauna: utilization of dredged material marshes in Galveston Bay, Texas, USA. Wetlands Ecol. Manage. 8(5):327–341.
Minello, T.J., J.R.Zimmerman, and E.F.Klima. 1987. Creation of fishery habitat in estuaries. Pp. 106–120 in Beneficial Uses of Dredged Materials, Proceedings of First Interagency Workshop, 7–9 October 1986, Pensacola, Florida, M.C.Landin and H.K.Smith, eds. Tech. Report D-87-1. Vicksburg, MS: U.S. Army Corps of Engineers.
Mitsch, W.J., and N.Flanagan. 1996. Comparison of Structure and Function of Constructed Deep water Marshes with Reference Freshwater Marshes. A study at the Des Plaines River Wetland Demonstration Project in northeastern Illinois. RF Project No. 729179, The Ohio State University Research Foundation, Columbus, OH.
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Montagna, P.A. 1993. Comparison of Ecosystem Structure and Function of Created and Natural Seagrass Habitats in Laguna Madre, Texas. Final Report. Tech. Report No. TR/93-007. Port Aransas, TX: University of Texas at Austin, Marine Science Institute.
Moy, L.D., and L.A.Levin. 1991. Are Spartina marshes a replaceable resources? A functional approach to evaluation of marsh creation efforts. Estuaries 14(1):1–16.
Niswander, S.F., and W.J.Mitsch. 1995. Functional analysis of a two-year-old created instream wetland: hydrology, phosphorus retention, and vegetation survival and growth. Wetlands 15(3):212–225.
Roberts, T.H. 1991. Habitat Value of Man-Made Coastal Marshes in Florida. Technical Report WRP-RE-2. Vicksburg, MS: U.S. Army Engineer Waterways Experiment Station.
Rulifson, R.A. 1991. Finfish utilization of man-initiated and adjacent natural creeks of South Creek Estuary, North Carolina using multiple gear types Estuaries 14(4):447–464.
Sacco, J.N., E.D.Seneca, and T.R.Wentworth 1994. Infaunal community development of artificially established salt marshes in North Carolina. Estuaries 17(2):489–500.
Shafer, D.J., and W.J.Streever 2000. A comparison of 28 natural and dredged material salt marshes in Texas with an emphasis on geomorphological variables. Wetlands Ecol. Manage. 8(5):353–366.
Simenstad, C.A., and R.M.Thom. 1996. Functional equivalency trajectories of the restored Gog-Le-Hi-Te estuarine wetland. Ecol. Applic. 6(1):38–57.
Streever, W.J. 2000. Spartina alterniflora marshes on dredged material: a critical review of the ongoing debate over success. Wetlands Ecol. Manage. 8(5):295–316.
Streever, W.J., K.M.Portier, and T.L.Crisman. 1996. A comparison of Dipterans from ten created and ten natural wetlands Wetlands 16(4):416–428.
Turner, R.E., J.M.Lee, and C.Neill. 1994. Backfilling canals to restore wetland: empirical results in coastal Louisiana. Wetlands Ecol. Manage. 3(1):63–78.
van Rees-Siewert, K.L., and J.J.Dinsmore. 1996. Influence of wetland age on bird use of restored wetlands in Iowa Wetlands 16(4):577–582.
Vose, F.E., and S.S.Bell. 1994. Resident fishes and macrobenthos in mangrove-rimmed habitats: evaluation of habitat restoration by hydrologic modification. Estuaries 17(3):585–596.
Zedler, J.B. 1990. A Manual for Assessing Restored and Natural Coastal Wetlands with Examples from Southern California. Report. No. T-CSGCP-021. La Jolla: California Sea Grant College.
Zedler, J.B., and J.C.Callaway. 1999. Tracking wetland restoration: do mitigation sites follow desired trajectories? Restor. Ecol. 7(1):69–73.
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Representative terms from entire chapter:
fresh marsh