Abstract
A simple mass flux model was developed to simulate the response of SO42- concentrations in surface waters to past and anticipated future changes in atmospheric deposition of SO42-. Values of bulk (or wet) SO42- deposition and dry deposition of S determined from measured air concentrations and a deposition velocity were insufficient to balance watershed SO42- export at the Hubbard Brook Experimental Forest, NH and for a regional survey of watersheds in the northeastern U.S. We propose two explanations for the unmeasured S source: I) a significant underestimation of dry S deposition, and/or 2) internal watershed S sources, such as weathering and/or mineralization of soil organic S. Model simulations based on these two mechanisms agreed closely with measured stream SO42- concentrations at Hubbard Brook. Close agreement between measured and model predicted results precluded identification of which of the two mechanisms controlled long-term trends in stream SO42-. Model simulations indicated that soil adsorption reactions significantly delayed the response of stream water to declines in SO42- inputs since 1970, but could not explain the discrepancy in watershed S budgets. Extrapolation of model predictions into the future demonstrates that uncertainty in the source of the S imbalance in watersheds has important implications for assessments of the recovery of surface water acid neutralizing capacity in response to anticipated future reductions in SO2 emissions.
Original language | English (US) |
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Pages (from-to) | 319-329 |
Number of pages | 11 |
Journal | Water, Air, and Soil Pollution |
Volume | 105 |
Issue number | 1-2 |
DOIs | |
State | Published - Jul 1998 |
Keywords
- Acid neutralizing capacity
- Hubbard Brook Experimental Forest
- Mass balance model
- Reduced SO emission
- Sulfur deposition
- Surface water sulfate
ASJC Scopus subject areas
- Environmental Engineering
- Environmental Chemistry
- Ecological Modeling
- Water Science and Technology
- Pollution