THE EFFECT OF SOIL CO2 ON DISSOLVED INORGANIC CARBON IN SHALLOW GROUNDWATER, KONZA PRAIRIE, NE KANSAS
Soil CO2 concentrations reached 7% in July to early August, when temperature was highest and moisture did not limit soil respiration, and dropped to less than 0.5% in March. δ13С of soil CO2 varied from -12.3 to -17.2 ‰ PDB with a mean of -14.8‰, which is typical for CO2 respired by warm-season grasses following the C4 photosynthetic cycle. Groundwater DIC demonstrated a seasonal trend from 7.0 to 9.0 mmol/L with the highest values late in the growing season. Groundwater δ13СDIC varied between -6.4 and -4.7 ‰ and was out-of-phase with DIC.
Carbon isotope enrichment of groundwater DIC relative to soil CO2 is explained by isotopic fractionation between CO2 and carbonate species in infiltrating water, and water-rock interaction. Calcite (average δ13С of 0 ‰) dissolution released additional HCO3- to the solution, contributing heavier carbon to DIC. Seasonal ranges of Ca2+ and δ13C in groundwater remained at nearly equilibrium conditions with calcite in a system open to CO2, based on C soil-horizon conditions over the study period. The highest soil pCO2 in summer months resulted in groundwater with the lightest isotopic composition; isotopic enrichment was less even though Ca2+ was highest from more active calcite dissolution. A lag time of 2-3 months between soil and groundwater CO2 maximas reflect a travel time of recharge water through the low-permeable unsaturated zone. Several samples, collected in early July with DIC up to 2 mmol/L lower than expected from the seasonal trend, were related to extreme storm events during which high streamwater rapidly recharged the aquifer and diluted groundwater.
One year of monitoring showed that soil CO2 and carbonate minerals are two main sources of shallow groundwater DIC at the Konza Prairie. The annual cycle of soil respiration controls seasonal variations of limestone weathering rates and the amount and isotopic composition of DIC. Long-term monitoring may show that increased respiration rates could result in higher carbon flux to groundwater.