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a Wetland Consultant, 24 Marshall Dr., Egg Harbor Township, NJ 08234
b Dep. of Natural Resource Sciences and L A, Univ. of Maryland, College Park, MD 20742. USDA-FAS, 1400 Independence Ave. SW, Washington, DC 20250
* Corresponding author (pedon{at}dnamail.com)
Two transects were established across submerging coastal landscapes in Dorchester County, Maryland. Extensive sampling protocol was performed along the submerging upland tidal marsh soils to model C sequestration. Coastal marsh soils are accreting vertically and migrating laterally over the low-lying forest soils to keep pace with sea-level rise. The predictive C sequestration model was a two-step linear function. Therefore, C sequestration will continue to occur by accumulation in the organic horizons and sea-level rise is the driving force. During the last 150 yr, the rate of C sequestration averaged 83.5 ± 23 g m2 yr1. Before the last few hundred years, the predicted long-term rate of C sequestration averaged 29.2 ± 5.35 g m2 yr1. Sampling protocol and model validation ascertain the validity of the model and placed 80% confidence and 10% accuracy on rates of C sequestration and the predictive model. The model indicated that coastal marsh soils have higher C storage capacity than upland forest soils, and soils in the Cumulic subgroup of Mollisols. In general, C storage in mineral soils tends to reach a steady-state condition, whereas C sequestration in coastal marsh soils is a continuous phenomenon. During the next century, future C sequestration in the newly formed coastal marsh soils averaged 400 ± 162 g m2 yr1. Modeling C sequestration in coastal marsh ecosystems indicated that C storage under positive accretionary balance acts as a negative feedback mechanism to global warming.
Abbreviations: MHW, mean high water
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J. L. Jespersen and L. J. Osher Carbon Storage in the Soils of a Mesotidal Gulf of Maine Estuary Soil Sci. Soc. Am. J., March 12, 2007; 71(2): 372 - 379. [Abstract] [Full Text] [PDF] |
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