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PERMFILE128524
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Last modified
8/24/2016 10:25:39 PM
Creation date
11/25/2007 6:16:20 PM
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Template:
DRMS Permit Index
Permit No
M1999002
IBM Index Class Name
Permit File
Doc Date
6/18/1999
Doc Name
GAMMA RAY AND SPECTRAL GAMMA RAY LOG
Media Type
D
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No
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- .II t. f, F.O LOf.ICAI. I::\TLKI'K LTATIO\ OF 11hLI. hO4J - <br />"fable 7.10 The abundance o(the radioact~lements and <br />their relative contributions to the overall radioactivity o(the <br />black. shale example o(Figure 7.1 I (values calculated for the <br />peak at 40m). ._ <br />Element Content *gamma tar % gamma ray <br />API equivalent value <br />Uranium I I ppm 89.OAP1 41.OSr <br />Thorium I S ppm 70.7 API 32.6'7c <br />Potassium 35% 57.1 API 26A%r <br />'using the multipliers given in the text (section 7.4) <br />Probably a more common way of introducing uranium <br />into sediments is in association with organic matter. I[ <br />has been established zxperimentall}~ that carbonaceous <br />material can extract uranium from solution very effi- <br />cizntl}', zspzcially over the range of pH 3.~-6.0 (acidic) <br />(Durrancz. 1986). Organic-rich shales often (but not <br />al+cays) contain large amounts of syngznetic uranium (i.e. <br />extracted locally), in which case the}' arz associated with <br />high gamma ray log values (e.g. Schmoker and Hester. <br />1983) (Figurzs 7.1, 7.22). It is the large size and high <br />charge density of the uran}•le ion which allows this, and it <br />is thought that the process eventually involvzs an ionic <br />bonding. The urano-organic complexes produced may <br />form coatings on organic or inorganic particlzs or be dis- <br />setninatzd through the sediment mass. However, the exact <br />relationship betwezn organic matter and total uranium <br />content is not easy to establish, since high organic matter <br />content is not always related to high uranium content (cf. <br />Meyer and Nederlof, 1934) (Figure 7.12). Empiricall}•, <br />[he constant presence of organic ma«er in shales (Table <br />7.11) suggests that uranium adsorbed by organic matter is <br />an impottant contributor to o+•erall shale radioactivity <br />(see Section 7.6). <br />The third way of introducing uranium into sediments <br />concerns principally phosphates and associated deposits. <br />The uranium present in phosphatic rocks is generally <br />syngenetic and is found within [he phosphates. Primary <br />uranium minerals are absent. The very variable valence <br />bzhaviour of uranium means that under the right condi- <br />tions it (omts complex ions with carbonate, phosphate, <br />hydroxide and others and it is assumzd that U" substi- <br />tutes (or calcium in the carbonate-fluorapatitz generally <br />found in marine phosphorites (Durrance, 1986). The <br />correct chemical conditions for this type of reaction may <br />be very localiszd, such as exist in hardgrounds. <br />[n general, uranium behaves as an independent <br />constituent: it is not chemically combined in thz principal <br />inoleculzs of rocks like potassium, but is looszly associ- <br />ated with secondary components. For this reason it has a <br />ver}~ heterogeneous distribution in sediments. Moreover, <br />its continued solubility even in thz subsur(acz, which is a <br />function of its loose attachments, rzndzrs it susceptible to <br />Izaching and redeposition, making its distribution even <br />morn irregular. <br />Table 7.11 Average weighl•of organic matter in sediments <br />(kom Shaw, 1980). <br />~ 3 <br />i <br />t y. <br />i <br />Sediment Average weight % <br />Shales 2.90 <br />Carbonates 0.29 <br />Sandstones 0.05 <br /> 'o <br />o <br />^ 0 <br /> o c+ <br />e~~~ <br /> 0 <br />0 0 <br />0 <br />0 0 <br />0 <br />0 <br />~o ao ao <br />ura ~~~n o~m <br />Figure 7.12 Organic carbon content compared to uranium <br />content: there is wide dispersion. (Source o(data. Adams and <br />\veaver, 1955). <br />Typically, on the logs, uranium is shown by irregular, <br />high peaks corresponding to its uneven distribution. Due <br />to the unusual requirements of its original deposition, <br />these peaks are associated with unusual environments <br />such as are found in condensed sequences or at unconfor- <br />mities (i.e. Figure 7.31). <br />Thorium <br />Like uranium, thorium has its origin principally in acid <br />and intermediate igneous rocks. However, i[ is exvemely <br />stable and, unlike uranium, will not go into solution. For <br />this reason it is found in bauxites (residual soils). <br />Although there is a possibility that thorium is adsorbed <br />onto clay minerals (Durrance, 1986), it is generally <br />transposed to sites of sediment deposition as clay fraction <br />detrital grains. These are of heavy minerals such as zir- <br />con, thorite, monazite, epidote and sphene (Table 7.12) <br />which are all very stable. <br />Because of its detrital nature and current vansport in <br />Table 7.12 Thorium-bearing heavy minerals (Serra er ul., 1980) <br /> Composition Thor content (%) <br />Thorite Th, Si, O, 25~i3 <br />Monazite Ce, Y, La, PO, 4-12 <br />Zircon Zr. Si. O, less than I <br /> Uranium ppm Thorium pm <br />Zircon 300.3000 100-2500 <br />Sphene 100-700 IOO~i00 <br />Epidote 20.50 50.500 <br />Apatite 5-I50 2-150 <br />76 <br />
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