Temporal variability of water quality was investigated at two springs in a karst aquifer in northern Alabama from 1999 to 2001. Hourly water temperature data for the smaller spring (discharge between 0.1 and 2 cubic feet per second) suggest this spring represents a shallow flow system with a relatively short average ground-water residence time. Water temperature fluctuated seasonally (16 ± 2 °C), with some spikes and dips in temperature occurring during storms. Water issuing from the larger spring (1 to 9 cubic feet per second) maintained a constant temperature (16 ± 0.2 °C) throughout the year. The larger spring represents a diffuse flow system having a longer average ground-water residence time than the smaller spring. Monthly water samples analyzed for major inorganic constituents from the two springs indicate variability in water quality, both seasonally and in response to storms. Decreases in specific conductance and calcite-saturation indices in samples from the smaller spring within several days of moderate rainfall indicate that spring discharge contains a component of water with short residence times. In contrast, an increase in specific conductance and calcite-saturation indices in samples from the larger spring after heavy rainfall indicate a contribution of water to the spring discharge with relatively long residence times. In samples from both springs, nitrate concentrations vary in response to an increase in recharge to the aquifer in the fall and early spring. Concentrations in the smaller spring also are affected by short-term dilution following storms. Pesticides were detected in all samples collected from the springs but concentrations generally were low (less than 1 microgram per liter). The herbicides fluometuron, atrazine, and their degradates were the most frequently detected pesticides. Fluometuron concentrations in samples from the smaller spring varied seasonally; however, fluometuron concentrations in samples from the larger spring did not fluctuate appreciably. In both springs, atrazine concentrations were highest after storms in the early spring. Variation of degradate concentrations was similar to the parent compounds.