BULLETIN NO. 68 Evaluation of the regional slope of the MFCU, lithologic similarities between the units, and sparse data for unit II lead to an alternate interpretation: unit II north of Manatee and Hardee Counties may correlate with unit VI south of these counties (Figure 39). In this interpretation, isolated MFCU facies occur approximately 400 ft (122 m) above the lower MFCU unit in southwestern Highlands and western Charlotte Counties. Plate 59 and Figure 39 (bottom half) reflect this latter interpretation. Wells that encountered both MFCU facies (II and VI) are represented by green symbols (Plate 59) and are labeled with the elevation of the shallower discontinuous MFCU facies, which is informally referred to as the "middle to upper Avon Park confining unit." Data in Miller (1988) indicate a high permeability zone between the base of the "middle to upper Avon Park confining unit" and the MFCU as mapped herein within all wells containing both of Miller's MFCU facies (II and VI). Based on comparison of Plate 38 with Miller's (1986) Middle Eocene isopach, the MFCU as defined and mapped in this study generally occurs within the lower half of the Avon Park Formation. Exceptions to the generalization include Marion, Osceola and Pinellas Counties, where the MFCU occurs within the upper third of the Avon Park Formation. Several cross sections contain wells that penetrate the MFCU (e.g., Plates 7, 9, 21, 29, 30 and 34). In the northwestern part of the study area, the elevation of the MFCU is generally deeper than -400 ft (-122 m) MSL. The unit dips southward to depths below -2100 ft (-640.1 m) MSL in Charlotte County. South of the study area, Reese (2000) mapped the "dolomite-evaporite unit in the middle confining unit" of the FAS, recognizing the significance of dense unfractured dolostones in his study area. He also notes that this unit may locally be considered the top of the MFCU, which is generally supported by the MFCU surface in Plate 59. It is possible that the few wells with shallower elevations in Reese's (2000) "dolomite evaporite unit" map are related to the discontinuous "middle to upper Avon Park confining unit" described herein. Presence of the MFCU is debatable for two regions within the eastern half of the study area. Throughout most of Marion County (including parts of Alachua, Sumter and Lake Counties), the MFCU is inferred. Borehole cuttings from multiple wells in the area show no evidence of gypsum/anhydrite; however, anomalously high sulfate concentrations (some exceeding 500 mg/L; Sacks, 1996) in FAS groundwater samples suggest the MFCU may be present. As such, this area is denoted on Plate 59 as "MFCU inferred based on water quality data." In eastern Polk County, Miller (1986) mapped the MFCU; however, available well control (this study and Miller, 1988), as well as water quality data for the area, yields no direct evidence that it is present. Sprinkle (1989) and Katz (1992) report relatively low sulfate concentrations (< 50 mg/L) within the UFA in the area. To emphasize this uncertainty the MFCU in this area is labeled "MFCU possibly absent: limited data" (Plate 59). Hydraulic conductivity analyses of MFCU rocks were not completed for this study; however, data exists in SWFWMD and consultant's reports. For example, Hickey (1982) reports hydraulic conductivities ranging from 1.1 ft/day to 6.0x10-7 ft/day (3.8x10-4 to 2. lxl0 10 cm/sec) based on core representing the "lower confining bed" (greater than -1000 ft [-305 m] MSL) in Pinellas County. To provide characterization of MFCU hydraulic conductivity and total porosity, data has been compiled from three injection well sites: Knight's Trail, Sarasota County, (Law Environmental, Inc., 1989), Burnt Store Utilities, Charlotte County, (ViroGroup, Inc., 1995) and Punta Gorda, Charlotte County, (City of Punta Gorda, Water Resource Solutions, Inc., and Boyle Engineering Corporation, 2001). Data from Stewart (1966) and Hickey (1982) and Montgomery Watson Americas (1997) are also included. Hydraulic conductivity (Kv) for the 21 MFCU cores analyzed in these studies range from 1.5x10-'1 ft/day to 1.Oxl0-6 ft/day (5.3x10-' to 3.53x10-10 cm/sec), with a median value of 1.84x10-3 ft/day (6.5x10-7 cm/sec; Figure 40). Total porosity for these samples average 17.2 percent (median = 19.6 percent) and range from 5 percent to 30 percent (Figure 41). Basso (2002) reports Kh values ranging from .002 to .04 ft/day (7.06x10-07 to 1.4x105 cm/sec). Transmissivity data range from 0.08 to 2.9 ft2/day (0.86 to 31.2 m2/day).