TY - JOUR
T1 - Precipitation change and soil leaching
T2 - Field results and simulations from walker branch watershed, Tennessee
AU - Johnson, D. W.
AU - Hanson, P. J.
AU - Todd, D. E.
AU - Susfalk, R. B.
AU - Trettin, C. F.
PY - 1998/7
Y1 - 1998/7
N2 - To investigate the potential effects of changing precipitation on a deciduous forest ecosystem, an experiment was established on Walker Branch Watershed, Tennessee that modified the amount of throughfall at -33%, ambient (no change), and +33% using a system of rain gutters and sprinklers. We hypothesized that the drier treatments would cause: 1) disproportionate changes in soil water flux, 2) increased total ionic concentrations in soil solution that would in turn cause 3) decreased SO42-/Cl- ratios, 4) decreased HCO3- concentrations, and 5) increased ratios of Al to (Ca2+ + Mg2+) and of(Ca2+ + Mg2+) to K+. Hypothesis 1 was supported by simulation results. Hypotheses 2 and 3 were supported in part by field results, although interpretation of these was complicated by pre-treatment biases. Hypotheses 4 and 5 were not supported by the field results. Comparisons of field data and Nutrient Cycling Model (NuCM) simulations were favorable for most ions except Cl- and K+. The disparities may be due to underestimation of soil buffering in the case of Cl- and overestimation of soil buffering in the case of K+ in the model. Long-term simulations with NuCM suggest that reducing water inputs will slow the rate of soil acidification and P loss, but will not materially affect growth or ecosystem N status.
AB - To investigate the potential effects of changing precipitation on a deciduous forest ecosystem, an experiment was established on Walker Branch Watershed, Tennessee that modified the amount of throughfall at -33%, ambient (no change), and +33% using a system of rain gutters and sprinklers. We hypothesized that the drier treatments would cause: 1) disproportionate changes in soil water flux, 2) increased total ionic concentrations in soil solution that would in turn cause 3) decreased SO42-/Cl- ratios, 4) decreased HCO3- concentrations, and 5) increased ratios of Al to (Ca2+ + Mg2+) and of(Ca2+ + Mg2+) to K+. Hypothesis 1 was supported by simulation results. Hypotheses 2 and 3 were supported in part by field results, although interpretation of these was complicated by pre-treatment biases. Hypotheses 4 and 5 were not supported by the field results. Comparisons of field data and Nutrient Cycling Model (NuCM) simulations were favorable for most ions except Cl- and K+. The disparities may be due to underestimation of soil buffering in the case of Cl- and overestimation of soil buffering in the case of K+ in the model. Long-term simulations with NuCM suggest that reducing water inputs will slow the rate of soil acidification and P loss, but will not materially affect growth or ecosystem N status.
KW - Leaching
KW - Nutrient Cycling Model
KW - Rainfall
KW - Soil solution chemistry
KW - Walker Branch Watershed
UR - http://www.scopus.com/inward/record.url?scp=0032127232&partnerID=8YFLogxK
U2 - 10.1023/A:1005039711434
DO - 10.1023/A:1005039711434
M3 - Article
AN - SCOPUS:0032127232
SN - 0049-6979
VL - 105
SP - 251
EP - 262
JO - Water, Air, & Soil Pollution
JF - Water, Air, & Soil Pollution
IS - 1-2
ER -