Improving the Success of Wetland Creation and Restoration with Know‐How, Time, and Self‐Design

The creation and restoration of new wetlands for mitigation of lost wetland habitat is a newly developing science/technology that is still seeking to define and achieve success of these wetlands. Fundamental requirements for achieving success of wetland creation and restoration projects are: understanding wetland function; giving the system time; and allowing for the self-designing capacity of nature. Mitigation projects involving freshwater marshes should require enough time, closer to 15-20 yr than 5 yr, to judge the success or lack thereof. Restoration and creation of forested wetlands, coastal wetlands, or peatlands may require even more time. Ecosystem-level research and ecosystem modelling development may provide guidance on when created and restored wetlands can be expected to comply with criteria that measure their success. Full-scale experimentation is now be- ginning to increase our understanding of wetland function at the larger spatial scales and longer time scales than those of most ecological experiments. Predictive ecological mod- elling may enable ecologists to estimate how long it will take the mitigation wetland to achieve steady state.

[1]  F. Sklar,et al.  Articulation, accuracy and effectiveness of mathematical models: A review of freshwater wetland applications☆ , 1985 .

[2]  K. Havens,et al.  An assessment of ecological conditions in a constructed tidal marsh and two natural reference tidal marshes in coastal Virginia , 1995 .

[3]  William J. Mitsch,et al.  Ecological Engineering A Cooperative Role with the Planetary Life-Support System , 1993 .

[4]  L. B. Leopold,et al.  Water In Environmental Planning , 1978 .

[5]  G. Barrett,et al.  Effects of vegetation and hydrologic load on sedimentation patterns in experimental wetland ecosystems , 1994 .

[6]  William G. Crumpton,et al.  Factors affecting nitrogen loss in experimental wetlands with different hydrologic loads , 1994 .

[7]  Barbara L. Bedford,et al.  The Need to Define Hydrologic Equivalence at the Landscape Scale for Freshwater Wetland Mitigation , 1996 .

[8]  Wetlands restoration and mitigation policies: Comment , 1986 .

[9]  Robert W. Nairn,et al.  Phosphorus Retention in Constructed Freshwater Riparian Marshes , 1995 .

[10]  C. Walters,et al.  Uncertainty, resource exploitation, and conservation: lessons from history. , 1993, Science.

[11]  D. Hey,et al.  Water quality improvement by four experimental wetlands , 1994 .

[12]  W. Mitsch,et al.  Creating freshwater marshes in a riparian landscape: research at the Des Plaines River Wetlands demonstration project , 1994 .

[13]  Robert Costanza,et al.  Developing Ecological Research That is Relevant for Achieving Sustainability. , 1993, Ecological applications : a publication of the Ecological Society of America.

[14]  M. Quammen Measuring the success of wetlands mitigation , 1986 .

[15]  W. Mitsch,et al.  Creation and Restoration of Wetlands: Some Design Consideration for Ecological Engineering , 1992 .

[16]  William J. Mitsch,et al.  Periphyton productivity on artificial and natural surfaces in constructed freshwater wetlands under different hydrologic regimes , 1994 .

[17]  L. Roberts Wetlands Trading Is a Loser's Game, Say Ecologists. , 1993, Science.

[18]  William J. Mitsch,et al.  Sediment deposition patterns in restored freshwater wetlands using sediment traps , 1994 .

[19]  Mary E. Kentula,et al.  Trends and patterns in section 404 permitting requiring compensatory mitigation in Oregon and Washington, USA , 1992 .

[20]  Robert H. Kadlec,et al.  Detention and mixing in free water wetlands , 1994 .

[21]  C. S. Holling,et al.  Investing in Research for Sustainability. , 1993, Ecological applications : a publication of the Ecological Society of America.

[22]  T. R. Wentworth,et al.  Designation of Wetlands by Weighted Averages of Vegetation Data: a Preliminary Evaluation , 1988 .