
|
|
publications > paper > PP 1403-G > ground-water movement > movement based on natural isotopes > carbon isotopes
Hydrogeology, Ground-Water Movement, and Subsurface Storage in the Floridan Aquifer System in Southern FloridaBy Frederick W. Meyer
Ground-Water Movement in the Floridan Aquifer System in Southern Florida: Ground-Water Movement Based on Natural Isotopes as TracersCarbon IsotopesThe radiocarbon dating technique has been an important and accepted research tool in archeology and geology since its inception in 1946 by Libby (1955). However, its use in hydrogeology has been dubious because of the uncertainties in comparing the carbon-14 in dissolved carbon species in ground water with respect to that in the water when it was last in contact with the atmospheric reservoir of carbon-14. An understanding of the involved chemical processes and the reservoir through which the ground water moves is essential to the interpretations and corrections that would apply to the measured carbon-14 in the sample. Carbon-14 measurements by the U.S. Geological Survey were by liquid scintillation counting of benzene which was synthesized from the carbonate in a 30-gallon (gal) sample of ground water (Pearson and Bodden, 1975; Thatcher and others, 1977); however, measurements by the Tritium Laboratory, Rosenstiel School of Marine and Atmospheric Sciences, University of Miami, were by gas proportional counting of carbon dioxide from a 55-gal water sample (Stuiver and Ostlund, 1980). By convention, the measurements were compared with standard National Bureau of Standards oxalic acid to determine the relative activity (R) for age-dating. The carbon-13/carbon-12 stable isotope ratio (
where the normalized activity, D14C, equals the determined activity, d14C, corrected for isotopic fractionation, assuming that a carbon-13/carbon-12 change from the accepted value for wood ( The percent of modern carbon (PMC), corrected for isotopic fractionation normalization or the percentile difference, was calculated using the following equation:
where s D14C/10 is the standard error. The age of the sample is expressed as apparent age owing to the uncertainty about past production of carbon-14 and the origin of the carbon in the water. The apparent age is based on the Libby half-life of 5,568 yr and was calculated using the following equation: Apparent age (before 1950) = -8033 ln (PMCx10-2) (5) The measured relative carbon-14 activities, R (that is, uncorrected for isotopic fractionation normalization), ranged from about 0.04 to 65.9 percent, and the normalized activities, PMC, ranged from about 0.04 to 62.9 percent. The experimental error for the analyses by the U.S. Geological Survey ranged from 0.2 to 1.5 percent, and that for the Tritium Laboratory, University of Miami, ranged from 0.1 to 0.3 percent. The corrections for isotopic fractionation normalization had relatively insignificant effects on the activities of the samples. No corrections for dilution or chemical reaction during transit were applied; therefore, the activities do not represent absolute age. Ages calculated according to equation 5 are maximum estimates. Corrections for reactions led to younger age estimates. However, insufficient data are available to correct PMC for reaction effects. Generally, the samples of brackish ground water from the Upper Floridan aquifer had lowest carbon-14 activities. Upper Floridan Aquifer The PMC (carbon-14 activity corrected for isotopic fractionation normalization) of samples of brackish ground water from the Upper Floridan aquifer at sites 5, 9, 10, 12, and 14 (table 4) ranged from about 0.04 (a value that is near the limit of the dating technique) to 16.7 percent. The stable isotope ratios ( Variations in the PMC with depth are indicated. At site 10, location of the Alligator Alley test well, the PMC of samples between 895 and 1,618 ft ranged from 4.5 to 16.7 percent and the carbon-13 stable isotope ratios ( At site 5 (well STL-255), the PMC for samples of brackish ground water from depths of about 898 to 1,663 ft in the Upper Floridan aquifer were virtually zero (0.18 and 0.04 percent), and the respective carbon-13 stable isotope ratios were -3.3 and 4.3
The cause of the apparent reversal in carbon-14 activity is unclear, but at least two hypotheses are possible. The first hypothesis requires the inland flow of seawater in the lower part of the Floridan aquifer system, as proposed by Kohout (1965) and supported by the isotope data in this report. This hypothesis is supported by the evidence that carbon-14 activity in water in the Upper Floridan aquifer decreases southward from central Florida. The reduction of carbon-14 activity is due to radioactive decay during the residential time and to dilution by inorganic carbon from limestone and dolomite in transit from central Florida toward the area of Lake Okeechobee. Beyond Lake Okeechobee, the southward-flowing water is blended with younger seawater from the Lower Floridan aquifer, and ground water in the Upper Floridan aquifer becomes brackish. As the ground water continues flowing generally southward toward the coastal areas, it becomes increasingly salty and contains greater amounts of carbon-14 as more seawater is contributed from the Lower Floridan aquifer. Thus, the carbon-14 activities in ground water decrease from central Florida to the area around Lake Okeechobee and then increase again southward from the lake. This hypothesis also is supported by the vertical distribution of carbon-14 in the Alligator Alley test well. The second hypothesis assumes that horizontal and vertical permeability in the system is highly variable, and that velocity differences are the chief cause of the apparent reversal in carbon-14 activity. If the permeability is assumed to be greatest along a flow line roughly from Polk City in central Florida to site 14 in southern Florida, then the time of travel along that line is assumed to be the least. Rates of ground-water flow in central Florida estimated by Hanshaw and others (1965) and modified by Plummer (1977) ranged from about 6 to 32 feet per year (ft/yr); therefore, the transit time from the central Florida recharge area at Polk City (33.4 percent of modern carbon) to the Alligator Alley test well (site 10) in southern Florida (4.5 percent of modern carbon), a distance of about 150 mi, could range from 132,000 to 24,750 yr. On the basis of the measured activity at Polk City and a rate of 32 ft/yr (the highest rate), the carbon-14 activity at site 10 (the Alligator Alley test well) in southern Florida would be about 1.5 percent of modern carbon, compared with the measured value of 4.5 percent. Also, the analysis does not consider the chemical reactions that would have occurred in transit and reduced the concentration of carbon-14 by dilution to less than 1.5 percent. The measured carbon-14 activity at site 10 (4.5 percent) is probably lower than the actual activity as a result of dilution while in transit. The results of this sample analysis suggest that either the velocity greatly exceeds 32 ft/yr or significant amounts of carbon-14 enter the flow system downgradient from Polk City and closer to site 10. Possible sources of closer freshwater recharge are the sinkhole lakes about 80 mi north-northwest of site 10 in southern Highlands County (Kohout and Meyer, 1959). By comparison, the first hypothesis seems to be the most plausible because the second hypothesis needs two constrained assumptions. However, more data are required to test these hypotheses. The distribution of Attempts to adjust the measured carbon-14 activities in the samples from southern Florida, using the chemical dilution and isotopic dilution methods suggested by Mook (1980, p. 58), yielded adjusted ages that seem to be inconsistent with the time-of-travel estimates. No attempts were made to use mass-balance and mass transfer calculation schemes, as suggested by Plummer (1977) and Wigley and others (1978), to adjust the measured carbon-14 activity or Lower Floridan Aquifer The carbon-14 activities, presented by percent of modern carbon (PMC), of samples of salty (salinity comparable to seawater) ground water from the Lower Floridan aquifer ranged from less than 0.69 to 62.9 percent (table 4). Of the eight samples, only four are considered representative of the native ground water. Apparently, four samples were contaminated with salty drilling fluid. At site 10, for example, three samples from the Lower Floridan aquifer had activities of about 29.0, 7.3, and 37.1 percent. The sample of October 19, 1981, which had an unusually high chloride concentration (22,700 mg/L) and the least carbon-14, probably contained residual, artificially produced, salty drilling fluid. The artificial drilling fluid was chiefly artesian water from the Upper Floridan aquifer and sodium chloride. Likewise, three samples collected at site 9 yielded activities of about 0.69, 1.12, and 62.9 percent. The samples of October 21, 1981, and December 16, 1982, which had low carbon-14 activities, were from an isolated zone in a deep monitor well (G-2331) that apparently had not been completely flushed of artificially produced drilling fluid. However, the sample of April 28, 1983, which had the highest carbon-14 activity, was pumped at a high rate (10,000 gal/min) from a nearby municipal wastewater disposal well (G-2333) and is, therefore, considered representative of the native fluid (a conclusion that is supported by the concentrations of uranium isotopes). The normalized carbon-14 activities (PMC) and the carbon-13/carbon-12 stable isotope ratios ( The apparent age of the saltwater in the Lower Floridan aquifer increases radially inland from site 9, suggesting that seawater enters the aquifer chiefly through submerged karst in the Straits of Florida, east of Fort Lauderdale, and then travels inland through highly permeable dolostones (chiefly the Boulder Zone). The rate of movement between sites 9 and 10 is about 44.5 mi in about 4,300 yr, or about 54.6 ft/yr, an average rate that greatly exceeds Hanshaw and others' (1965) estimated range in average rates (7 to 39 ft/yr) for the Upper Floridan aquifer in central Florida. Most of this difference is probably due to the extremely high transmissivity of the Lower Floridan aquifer (Boulder Zone). The rate of ground-water movement between the subsea outcrop (karst of the Miami Terrace) in the Straits of Florida and site 9 at Fort Lauderdale is about 10.5 mi in about 3,200 yr, or about 17.3 ft/yr; the rate between the subsea outcrop and site 10 is about 55.0 mi in about 7,500 yr, or about 38.7 ft/yr. The relative increase in rates of movement with distance inland from the source suggests that inland movement of seawater through the highly permeable zones of the Lower Floridan aquifer could be related in part to the rapid rise of sea level during the Holocene transgression. The effects of changing sea level on ground-water movement and hydraulic gradients in the Lower Floridan aquifer are discussed in a later section of this report.
Previous: < Ground-Water Movement - Movement Based on Natural Isotopes | Next: Uranium Isotopes > |
U.S. Department of the Interior, U.S. Geological Survey
This page is: http://sofia.usgs.gov/publications/papers/pp1403g/carbon.html
Comments and suggestions? Contact: Heather Henkel - Webmaster
Last updated: 06 January, 2005 @ 11:02 AM(TJE)