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these wind patterns. Accordingly, the environmental samPliny <br />location proximate to tl~e west property boundary is located <br />such that it is virtually unaffected by the valley wind <br />patterns and is expected to yield airborne particulate <br />concentrations uninfluenced by the licensed facilities. <br />IV. Pathways <br />A. External Dose - Direct Gamma Radiation <br />The mineralc~yy surrou m.li n~~ tl~c ltcruse:J f~~~rlitirs make., tlir <br />determination of a "i~et" dose for ga«uua tedtation trom th~_ <br />licensed facilities difficult. The mineralogy of tl~e ot,t,osiny <br />valley slopes at the Sttr is quite different. Specificall:~, <br />the valley side east-northeast of the site is much young e!: <br />than the valley side nest-northwest of the site. The age .it <br />the east-northeast side is on the order of millions of years, <br />while the west-northwest side is about 4 to 4.5 billion y.-ars <br />old. Needless to say, this leads to a vastly different <br />mineralogy. The east-northeast side is comprised mostly o1: <br />sandstones, mudstones, clay and conglomerates, while the <br />west-northwest side is made up of metamorphosed gneisses <~~td <br />schists. Geology types such as sandstones, mudstones, and <br />clays are historically associated with higher "background" <br />gamma counts than the metamorphosed types. <br />This difference in mineralogy substantially limits the usc~ of <br />a thermoluminescent dosimeter (TLD) for background <br />subtraction. To address this problem, Cotter proposed the <br />placement of ten TLDs on the east-northeast valley side for a <br />period of one year. This proposal was approved by Radiation <br />Control and monitoring began on April 1, 1988. The one year <br />monitoring period was completed in 1989 and the average <br />annual background gamma radiation exposure for the ten <br />locations studied was 184 mRem. <br />A gamma dose is not attributed to the licensed facilities and <br />is not included to the ottsite dose conunitment because the <br />background study data of 184 mRem/year exceads the pro7ecteri <br />173.6 mRem/year from monitoring data cc11CC•ted from January <br />through June 1993 (81.8 mRem) and the previous six months for <br />the environmental sampling location which approximates the <br />nearest feasible resident. <br />