Abstract
A major obstacle to assessing functional equivalency of restored or created wetlands is the time needed to develop the functions of natural wetlands. We compared hydrologic, water-quality, and vegetation-composition functions of nine natural coastal plain ponds in the New Jersey Pinelands with those of four small, well-established excavated basins that are at least 50 years old. Our study revealed that well-established (> 50 yr old) excavated ponds achieved a moderate degree of functional equivalency with Pinelands wetlands, representing a range of coastal plain pond characteristics. Based on water-depth-fluctuation patterns and the similarity of most hydrologic indices, including high-water pond area, mean water depth, area of exposed substrate (drawdown), and the presence of a clay lens, the excavated ponds seemed to achieve hydrologic equivalency with the natural reference wetlands. However, steeper bank slopes found at most of the excavated ponds affected nearshore water depths and resulted in the absence of plant zonation that characterizes coastal plain ponds. The water-quality function, represented by pH, specific conductance, and total organic carbon, differed between pond types. The pH and specific conductance of the excavated ponds were higher and total organic carbon concentrations were lower compared with the natural ponds. We attributed these differences to landscape setting, reflected by adjacent vegetation and contrasting plant zonation. Elevated specific conductance values in the natural ponds were likely due to the higher hydrogen ion concentrations. Reduced light transmission due to higher organic carbon concentrations in the natural ponds may have greater ecological importance. However, differences in water-quality functions between the pond types may make excavated ponds more prone to changes in pH if constructed within landscapes with extensive developed or agricultural lands. The excavated ponds met or exceeded most vegetation-composition reference criteria associated with the natural wetlands. Total and herbaceous species richness were greater in the excavated ponds. Most importantly, the excavated ponds supported a native Pinelands species composition, thus preserving regional biodiversity. Because all ponds were acidic and displayed pH values within the range associated with native Pinelands plants, differences in pH may not have been the cause of the greater species richness. Although overall species composition differed between the two pond types, the flora of the created wetlands was similar to that of coastal plain ponds found in other regions and other areas of the Pinelands. The major difference in vegetation composition between ponds was both the lack of distinct vegetation zonation due to steeper slopes and lower patch-type diversity in the excavated ponds. These structural differences can be overcome by constructing ponds with slopes that are comparable to natural ponds. Because the transitional-upland location of the excavated ponds is a more likely location for a mitigation wetland, the effect of landscape setting on water quality may not be as easily remedied as the lack of nearshore slopes.
Similar content being viewed by others
Literature Cited
Applegate, J. E., S. Little, and P. E. Marucci. 1979. Plant and animal products of the Pine Barrens, p. 25–36.In R. T. T. Forman (ed.) Pine Barrens: Ecosystem and Landscape. Academic Press, New York, NY, USA.
Ballard, J. T. 1979. Fluxes of water and energy through the Pine Barrens ecosystems. p. 133–146.In R. T. T. Forman (ed.) Pine Barrens: Ecosystem & Landscape. Academic Press, New York, NY, USA.
Bedford, B. L. 1996. The need to define hydrologic equivalence at the landscape scale for freshwater wetland mitigation. Ecological Applications 6:57–68.
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 16:532–541.
Brinson, M. M. 1993. Changes in the functioning of wetlands along environmental gradients. Wetlands 13:65–74.
Brinson, M. M. and R. Rheinhardt. 1996. The role of reference wetlands in functional assessment and mitigation. Ecological Applications 6:69–76.
Bunnell, J. F. and R. A. Zampella. 1999. Acid water anuran pond communities along a regional forest to agro-urban ecotone. Copeia 1999;614–627.
Clymo, R. S. 1963. Ion exchange inSphagnum and its relation to bog ecology. Annals of Botany 27:309–324.
Confer, S. R. and W. A. Niering. 1992. Comparison of created and natural freshwater emergent wetlands in Connecticut (USA). Wetlands Ecology and Management 2:143–156.
Eck, P. 1990. The American Cranberry. Rutgers University Press, New Brunswick, NJ, USA.
Ehrenfeld, J. G. 1983. The effects of changes in land-use on swamps of the New Jersey Pine Barrens. Biological Conservation 25:353–375.
Ehrenfeld, J. G. and J. P. Schneider. 1991.Chamaecyparis thyoides wetlands and suburbanization: effects on hydrology, water quality and plant community composition. Journal of Applied Ecology 28:467–490.
Ehrenfeld, J. G. and J. P. Schneider. 1993. Responses of forested wetland vegetation to perturbations of water chemistry and hydrology. Wetlands 13:122–129.
Fernald, M. L. 1950. Gray's Manual of Botany, eighth edition. Dioscorides Press, Portland, OR, USA.
French, H. M. and M. Demitroff. 2001. Cold-climate origin of the enclosed depressions and wetlands (‘Spungs’) of the Pine Barrens, southern New Jersey, USA. Permafrost and Periglacial Processes 12:337–350.
Forman, R. T. T. 1979. Fine Barrens: Ecosystem and Landscape. Academic Press, New York, NY, USA.
Gagnon, Z. E. and J. M. Glime. 1992. The pH-lowering ability ofSphagnum magellanicum Brid. Journal of Bryology 17:47–57.
Gleason, H. A. and A. Cronquist. 1991. Manual of Vascular Plants of Northeastern United States and Adjacent Canada, second edition. New York Botanical Garden, Bronx, NY, USA.
Godfrey, R. K. and J. W. Wooten. 1981. Aquatic and Wetland Plants of Southeastern United States—Dicotyledons. University of Georgia Press, Athens, GA, USA.
Hill, M. O. 1979a. DECORANA—A FORTRAN program for detrended correspondence analysis and reciprocal averaging. Cornell University, Ithaca, NY, USA.
Hill, M. O. 1979b. TWINSPAN—A FORTRAN program for arranging multivariate data in an ordered two-way table by classification of the individuals and attributes. Cornell University. 1th-aca, NY, USA.
Hill, M. O. and H. G. Gauch, Jr. 1980. Detrended correspondence analysis: an improved ordination technique. Vegetatio 42:47–58.
Johnsson, P. A. and J. L. Barringer. 1993 Water quality and hydrogeochemical processes in McDonalds Branch basin, New Jersey Pinelands, 1984–1988. U. S. Geological Survey Water-Resources Investigations Report 91-4081.
Kilham, P. 1982. The biogeochemistry of bog ecosystems and the chemical ecology ofSphagnum. The Michigan Botanist 21:159–168.
Kirkman, L. K., R. F. Lide, G. Wein, and R. R. Sharitz. 1996. Vegetation changes and land-use legacies of depression wetlands of the western coastal plain of South Carolina: 1951–1992. Wetlands 16:564–576.
Kirkman, L. K., P. C. Goebel, L. West, M. B. Drew, and B. J. Palik. 2000. Depressional wetland vegetation types: a question of plant community development. Wetlands 20:373–385.
Laidig, K. J. and R. A. Zampella. 1999. Community attributes of Atlantic white cedar (Chamaecyparis thyoides) swamps in disturbed and undisturbed Pinelands watersheds. Wetlands 19:35–49.
Laidig, K. J., R. A. Zampella, J. F. Bunnell, C. L. Dow, and T. M. Sulikowski. 2001. Characteristics of selected Pine Barrens treefrog ponds. Pinelands Commission, New Lisbon, NJ, USA.
Lord, D. G., J. L. Barringer, P. A. Johnsson, P. F. Schuster, R. L. Walker, J. E. Fairchild, B. N. Sroka, and E. Jacobsen. 1990. Hydrogeochemical data from an acidic deposition study at McDonalds Branch basin in the New Jersey Pinelands, 1983–86. U. S. Geological Survey Open-file Report 88-500.
McCarthy, K. A. 1987. Spatial and temporal distributions of species in two intermittent ponds in Atlantic County, New Jersey. M.S. thesis. Rutgers, The State University of New Jersey, New Bruns-wick, NJ, USA.
McCormick, J. 1979. The vegetation of the New Jersey Pine Barrens, p. 229–243.In R. T. T. Forman (ed.) Pine Barrens: Ecosystem and Landscape. Academic Press, New York, NY, USA.
McCune, B. and J. B. Grace. 2002. Analysis of Ecological Communities. MjM Software Design, Greneden Beach, OR, USA.
McCune, B. and M. J. Mefford. 1999. PC-ORD. Multivariate Analysis of Ecological Data, Version 4. MjM Software Design, Gleneden Beach, OR, USA.
Mitsch, W. J. and J. G. Gosselink. 1993. Wetlands, second edition. Van Nostrand Reinhold, New York, NY, USA.
Mitsch, W. J. and R. F. Wilson. 1996. Improving the success of wetland creation and restoration with know-how, time, and self-design. Ecological Applications 6:77–83.
Morgan, M. D. 1991. Sources of stream acidity in the New Jersey Pinelands. Verhandlungen Internationale Vereinigung Limnologie 24:1707–1710.
Morgan, M. D. and K. R. Philipp. 1986. The effect of agricultural and residential development on aquatic macrophytes in the New Jersey Pine Barrens. Biological Conservation 35:143–158.
Mueller-Dombois, D. and H. Ellenberg. 1974. Aims and methods of vegetation ecology. John Wiley and Sons, New York, NY, USA.
National Research Council. 1995. Wetlands: Characteristics and Boundaries. National Academy Press, Washington, DC, USA.
Newman, M. C. and J. F. Schalles. 1990. The water chemistry of Carolina bays: a regional survey. Archiv fur Hydrobiologie 118: 147–168.
Rheinhardt, R. D., M. M. Brinson, and P. M. Farley. 1999. Applying wetland reference data to functional assessment, mitigation, and restoration. Wetlands 17:195–215.
Rice, W. R. 1989. Analyzing tables of statistical tests. Evolution 43: 223–225.
Rhodehamel, E. C. 1979a. Geology of the New Jersey Pine Barrens. p. 39–60.In R. T. T. Forman (ed.) Pine Barrens: Ecosystem and Landscape. Academic Press, New York, NY, USA.
Rhodehamel, E. C. 1979b. Hydrology of the New Jersey Pine Barrens. p. 147–167.In R. T. T. Forman (ed.) Fine Barrens: Ecosystem and Landscape. Academic Press, New York, NY, USA.
Sass, K. 1992. Directory of New Jersey aerial photography. New Jersey Geological Survey, Trenton, NJ, USA. Geological Survey Report 30.
Schalles, J. F. and D. J. Shure 1989. Hydrology, community structure, and productivity patterns of a dystrophic Carolina bay wetland. Ecological Monographs 59:365–385.
Schneider, R. 1994. The role of hydrologic regime in maintaining rare plant communities of New York's Coastal Plain Pondshores. Biological Conservation 68:253–260.
Sharitz, R. R. and J. W. Gibbons 1982. The ecology of southeastern shurb bogs (pocosins) and Carolina bays: a community profile. U. S. Fish and Wildlife Service, Division of Biological Services, Washington, DC, USA. FWS/OBS-82/04.
Simenstad, C. A. and R. M. Thom. 1996. Functional equivalency trajectories of the restored Go-Le-Hi-Te estuarine wetland. Ecological Applications 6:38–56.
Sorrie, B. A. 1994. Coastal plain ponds in New England. Biological Conservation 68:225–233.
Smith, R. D., A. Ammann, C. Bartoldus, and M. M. Brinson. 1995. An approach for assessing wetland functions using hydrogeomorphic classification, reference wetlands, and functional indices. U.S. Army Engineers Waterways Experiment Station, Vicksburg, MS, USA. Technical Report WRP-DE-9.
StatSoft, Inc. 2000. Statistica for Windows. Tulsa, OK.
Stolt, M. H., M. H. Genthner, W. L. Daniels, V. A. Groover, S. Nagle, and K. C. Haering. 2000. Comparison of soil and other environmental conditions in constructed and adjacent palustrine reference wetlands. Wetlands 20:671–683.
Stone, W. 1911. The Plants of Southern New Jersey. Report of the New Jersey State Museum 1910. Trenton, NJ, USA.
Tedrow, J. C. F. 1979. Development of Pine Barrens soils, p. 61–79.In R. T. T. Forman (ed.) Pine Barrens: Ecosystem and Landscape. Academic Press, New York, NY, USA.
Tyndall, R. W., K. A. McCarthy, J. C. Ludwig, and A. Rome. 1990. Vegetation of six Carolina bays in Maryland. Castanea 55:1–21.
van der Valk, A. G. 1981. Succession in wetlands: A Gleasonian approach. Ecology 62:688–696.
van der Valk, A. G. and C. B. Davis. 1978. The role of seed banks in the vegetation dynamics of prairie glacial marshes. Ecology 59: 322–335.
Wetzel, R. G. 2001. Limnology: Lake and River Ecosystems, third edition. Academic Press, New York, NY, USA.
Wilson, R. F. and W. J. Mitsch. 1996. Functional assessment of five wetlands constructed to mitigate wetland loss in Ohio, USA. Wetlands 16:436–451.
Wolfe, P. E. 1953. Periglacial frost-thaw basins in New Jersey. Journal of Geology 61:133–143.
Zampella, R. A., G. Moore, and R. E. Good. 1992. Gradient analysis of pitch pine (Pinus rigida Mill.) lowland communities in the New Jersey Pinelands. Bulletin of the Torrey Botanical Club 119:253–261.
Zampella, R. A. 1994. Characterization of surface water quality along a watershed disturbance gradient. Water Resources Bulletin 30:605–611.
Zampella, R. A. and J. F. Bunnell. 1998. Use of reference-site fish assemblages to assess aquatic degradation in Pinelands streams. Ecological Applications 8:645–658.
Zampella, R. A. and K. J. Laidig. 1997. Effect of watershed disturbance on Pinelands stream vegetation. Journal of the Torrey Botanical Society 124:52–66.
Zampella, R. A., C. L. Dow, and J. F. Bunnell. 2001. Using reference sites and simple linear regression to estimate long-term water levels in Coastal Plain forests. Journal of the American Water Resources Association 37:1189–1201.
Zaremba, R. E. and E. E. Lamont. 1993. The status of the Coastal Plain Pondshore community in New York. Bulletin of the Torrey Botanical Club 120:180–187.
Zar, J. H. 1999. Biostatistical Analysis. Prentice Hall, Upper Saddle River, NJ, USA.
Zedler, J. B. 1996. Ecological issues in wetland mitigation: an introduction to the forum. Ecological Applications 6:33–37.
Author information
Authors and Affiliations
Rights and permissions
About this article
Cite this article
Zampella, R.A., Laidig, K.J. Functional equivalency of natural and excavated coastal plain ponds. Wetlands 23, 860–876 (2003). https://doi.org/10.1672/0277-5212(2003)023[0860:FEONAE]2.0.CO;2
Received:
Revised:
Accepted:
Issue Date:
DOI: https://doi.org/10.1672/0277-5212(2003)023[0860:FEONAE]2.0.CO;2