Distribution and turnover of carbon in natural and constructed wetlands in the Florida Everglades

Stable and radiocarbon isotopic contents of dissolved organic C (DOC), dissolved inorganic C (DIC), particulate organic C (POC) and plants were used to examine the source and turnover rate of C in natural and constructed wetlands in the Florida Everglades. DOC concentrations decreased, with P concentrations, along a water quality gradient from the agriculturally impacted areas in the northern Everglades to the more pristine Everglades National Park. d 13 C values of DOC in the area reflect contributions of both wetland vegetation and sugarcane from agriculture. Radiocarbon ages of DOC, POC and DIC in the Everglades ranged from 2.01 ka BP to ‘‘>modern’’. The old 14 C ages of DOC and POC were found in impacted areas near the Everglades Agricultural Area (EAA) in the northern Everglades. In contrast, DOC and POC in pristine marsh areas had near modern or ‘‘>modern’’ 14 C ages. These data indicate that a major source of POC and DOC in impacted areas is the degradation of historic peat deposits in the EAA. In the pristine areas of the marsh, DOC represents a mix of modern and historic C sources, whereas POC comes from modern primary production as indicated by positive D 14 C values, suggesting that DOC is transported farther away from its source than POC. High D 14 C values of DIC indicate that dissolution of limestone bedrock is not a significant source of DIC in the Everglades wetlands. As a restored wetland moves towards its ‘‘original’’ or ‘‘natural’’ state, the 14 C signatures of DOC should approach that of modern atmosphere. In addition, measurements of concentration and C isotopic composition of DOC in two small constructed wetlands (i.e., test cells) indicate that these freshwater wetland systems contain a labile DOC pool with rapid turnover times of 26–39 days and that the test cells are overall net sinks of DOC. � 2007 Elsevier Ltd. All rights reserved.

[1]  B. Gu,et al.  Limnological characteristics of a subtropical constructed wetland in south Florida (USA) , 2006 .

[2]  Mary Ann Moran,et al.  BACTERIAL UTILIZATION OF DISSOLVED HUMIC SUBSTANCES FROM A FRESHWATER SWAMP , 1997 .

[3]  P. Mccormick,et al.  Periphyton responses to experimental phosphorus enrichment in a subtropical wetland , 2001 .

[4]  T. Bianchi,et al.  Terrestrially derived dissolved organic matter in the Chesapeake Bay and the Middle , 2000 .

[5]  C. Richardson,et al.  Peat Accretion and N, P, and Organic C Accumulation in Nutrient-Enriched and Unenriched Everglades Peatlands. , 1993, Ecological applications : a publication of the Ecological Society of America.

[6]  R. Benner,et al.  What happens to terrestrial organic matter in the ocean , 1997 .

[7]  P. Grootes,et al.  Organic Carbon-14 in the Amazon River System , 1986, Science.

[8]  U. Zweifel,et al.  Factors controlling accumulation of labile dissolved organic carbon in the Gulf of Riga , 1999 .

[9]  Dennis A. Hansell,et al.  Mineralization of dissolved organic carbon in the Sargasso Sea , 1995 .

[10]  E. Tipping,et al.  Al(III) and Fe(III) binding by humic substances in freshwaters, and implications for trace metal speciation. , 2002 .

[11]  P. Raymond,et al.  Use of 14C and 13C natural abundances for evaluating riverine, estuarine, and coastal DOC and POC sources and cycling: a review and synthesis , 2001 .

[12]  J. Bauer,et al.  Utilization and turnover of labile dissolved organic matter by bacterial heterotrophs in eastern North Pacific surface waters , 1996 .

[13]  M. Chimney,et al.  Environmental impacts to the Everglades ecosystem: a historical perspective and restoration strategies. , 2001, Water science and technology : a journal of the International Association on Water Pollution Research.

[14]  C. Richardson,et al.  Recent and long-term organic soil accretion and nutrient accumulation in the Everglades , 1998 .

[15]  M. Stuiver,et al.  Discussion: Reporting of 14 C Data , 1977 .

[16]  J. Ogden,et al.  Everglades: The Ecosystem and Its Restoration , 1996 .

[17]  L. Harris,et al.  Everglades: The Ecosystem and its Restoration. , 1995 .

[18]  David G. Kinniburgh,et al.  ION BINDING TO NATURAL ORGANIC MATTER : COMPETITION, HETEROGENEITY, STOICHIOMETRY AND THERMODYNAMIC CONSISTENCY , 1999 .

[19]  R. Amundson,et al.  Potential for14C Dating of Biogenic Carbonate in Hackberry (Celtis) Endocarps , 1997, Quaternary Research.

[20]  M. Fogel,et al.  Seasonal and diel relationships between the isotopic compositions of dissolved and particulate organic matter in freshwater ecosystems , 2003 .

[21]  B. Forsberg,et al.  Autotrophic Carbon Sources for Fish of the Central Amazon , 1993 .

[22]  R. T. Wright,et al.  The distribution and stable carbon isotopic composition of dissolved organic carbon in estuaries , 1994 .

[23]  The use of radiocarbon measurements in atmospheric studies. , 1990 .

[24]  M. Rubin,et al.  Petroleum Pollutants in Surface and Groundwater as Indicated by the Carbon-14 Activity of Dissolved Organic Carbon , 1975, Science.

[25]  J. Vallino,et al.  Decomposition of dissolved organic matter from the continental margin , 2002 .

[26]  D. Canfield,et al.  Sources of particulate organic matter in rivers from the continental USA: Lignin phenol and stable carbon isotope compositions. , 2000 .

[27]  B. Voelker,et al.  Interpretation of metal speciation data in coastal waters: the effects of humic substances on copper binding as a test case , 2001 .

[28]  J. Stephens Subsidence of Organic Soils in the Florida Everglades1 , 1956 .

[29]  C. Richardson,et al.  Nutrient profiles in the everglades: examination along the eutrophication gradient. , 1997, The Science of the total environment.

[30]  D. Campbell,et al.  Chemical and carbon isotopic evidence for the source and fate of dissolved organic matter in the northern Everglades , 2002 .

[31]  P. Santschi,et al.  Organic nature of colloidal actinides transported in surface water environments. , 2002, Environmental science & technology.

[32]  S. Davis Growth, decomposition, and nutrient retention of Cladium jamaicense Crantz and Typha domingensis Pers. in the Florida Everglades , 1991 .

[33]  S. Epstein,et al.  Two Categories of 13C/12C Ratios for Higher Plants , 1971 .

[34]  J. Bauer,et al.  Isotopic constraints on carbon exchange between deep ocean sediments and sea water , 1995, Nature.

[35]  J. Ehleringer,et al.  Carbon Isotope Discrimination and Photosynthesis , 1989 .

[36]  K. Kalbitz,et al.  Different effects of peat degradation on dissolved organic carbon and nitrogen , 2002 .