FLORIDA GEOLOGICAL SURVEY and northeastern boundaries. Water levels declined about 5 feet in discharge areas (Hillsborough and Kissimmee River basins) because the ground-water discharge is relatively uniform regardless of seasonal variations in rainfall. Water levels declined less than 5 feet in the interior of the Green Swamp because there was little local pumpage and the rainfall during the dry period was about enough to balance the outflow; therefore, the aquifer remained relatively full. The area surrounding the Green Swamp is more populated and developed and increased pumping during the dry period (1962) caused a greater decline in piezometric levels than would have occurred under natural conditions. If there had been no appreciable increase in pumping, the map could be used to detect areal changes in the hydraulic characteristics of the aquifer, particularly changes in permeability. The northernmost extent of an area of heavy pumping for mining, industrial, municipal, and irrigational supplies is in the vicinity of Lakeland where the water levels declined about 20 feet. The drawdown is confined to the southern boundary of Green Swamp, suggesting that the area of the sinkhole-riddled ridges around southern Green Swamp is a recharge area. Water levels declined between 10 and 20 feet on the western side of Green Swamp in the vicinity of Dade City. This is considered to be an area of high permeability and good recharge. Water levels declined about 10 feet in the northeastern area which is also considered to be an area of high permeability and good recharge. The general conclusion is that increase in discharge (natural or pumping) does not appreciably increase the lateral movement of ground water from the interior of Green Swamp but does affect the border areas. HYDRAULICS OF THE FLORIDAN AQUIFER Coefficients of horizontal and vertical permeability were determined for selected core samples of the limestones that comprise the Floridan aquifer. The samples were obtained from well 805-154-8, located just north of Lake Parker. The laboratory determinations are presented in table 9. The permeability values ranged from 0.0001 to 19 gpd/ft2. The specific yields ranged from 0.2 to 23.2 percent. However, the specific yield determined in the laboratory represents that of the rock sample and not of the aquifer as confined.