Bacterial utilization of natural levels of dissolved organic carbon (DOC) was measured in the York River estuary, a sub-estuary of the Chesapeake Bay. This study was undertaken in order to elucidate spatial and temporal changes in bacterial carbon utilization and to evaluate its importance as a pathway for organic matter transformation in estuaries. Multiple pools of DOC were defined based on decomposition kinetics. The first pool (G 1 ) made up a mean of 2.8% of total DOC and had turnover times of ≤ 5 d. The second pool (G 2 ) comprised an average of 4.9% of total DOC and had turnover times of ~1 mo. Our data indicate that although the total amount of DOC utilized was low, there was a continual supply of both the G 1 and G 2 fractions within the estuary. Bacterial growth efficiency on the G 1 pool averaged 28%. The production of CO 2 through bacterial respiration of the G 1 pool could not balance CO 2 evasion for the majority of the estuary. Bacterial DOC degradation in the York River estuary was limited by temperature for the majority of the year. This temperature constraint coupled with relatively short hydrologic residence times resulted in the export of labile DOC from the estuary prior to complete bacterial decomposition. We estimate that ~10% of the riverine DOC exported annually from estuaries to the mid-Atlantic Bight (MAB) is a labile fraction of DOC that is not utilized within the estuaries due to temperature constraints on estuarine bacteria. This DOC is not inherently recalcitrant and is an allochthonous source of labile DOC for the coastal MidAtlantic Ocean.KEY WORDS: Dissolved organic carbon (DOC) · Heterotrophy · Mid-Atlantic Bight · Carbon export · Chesapeake Bay · York River
Resale or republication not permitted without written consent of the publisherAquat Microb Ecol 22: [1][2][3][4][5][6][7][8][9][10][11][12] 2000 This continuum of reactivity is described in the multi-G model (Berner 1980, Westrich & Berner 1984, where the decay (i.e., removal) of organic matter is dictated by the sequential loss of discrete pools with decreasing decay constants. Previous studies have not generally observed a relationship between DOC concentrations and indicators of bacterial activity and growth (i.e., bacterial production and abundance) in rivers and estuaries (Findlay et al. 1996, Basu & Pick 1997. This may be due, in part, to the continuum of reactivity within the DOC pool, because it is sometimes a small percentage of the DOC pool that supports the majority of bacterial carbon utilization (Wright & Hobbie 1965, Kirchman et al. 1991, but see Amon & Benner 1996. Søndergaard & Middelboe (1995) found that the average percentage of labile (defined as the amount utilized in ≤ 7 d) DOC in lakes, rivers, and marine systems was 14, 19, and 19% of the total DOC pool, respectively. Across systems the concentration of labile DOC generally increased with increasing total DOC concentrations, with an average response of an additional 0.17 µM labile DOC for every 1.0 µM increase in total DOC (Søndergaard & ...