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<. <br /> WIWI <br /> k <br /> Prior to sampling, the well was developed by purging a total <br /> of one well casing volume. Develcp-ent volumes were reduced <br /> from the five used in Phase I, to one, when it became apparent <br /> .� that neither well was capable of yielding significant amounts <br /> of water. Development water was periodically monitored for ph <br /> and electrical conductivity, and drummed onsite for ultimate <br /> disposal pending analytical results. <br /> !" A ground water sample from each well was collected immediately <br /> after development. Upon collection, groundwater samples were <br /> 1a stored on ice, and delivered that day to Anlab, Sacramento, <br /> 1s for chemical analyses. <br /> V4 <br /> 4 . 2 LITHOLOGIC SEQUENCE AND FIRST GROUNDWATER <br /> Boring logs fcr all three monitor weds are presented in the <br /> 1� <br /> Appendix. Briefly, the subsurface strata consist primarily. of <br /> sandy clays and silty sands of variable moisture content <br /> through a depth of 95 feet. <br /> &.:4 For MW-1 , both coarsest lithologic units and elevated HNu <br /> readings, as shown in Table 4-2 and Figure 4-3, were <br /> associated primarily with the depth interval 65--75 ft, and <br /> served as the basis for setting the well screen interval at a <br /> 14 depth sufficient to intersect this lithologic sequence. It <br /> should be noted however, that HNu instrument malfunction <br /> Prevented 1,1D readings over the entire boring (during Phase <br /> fY 1 ) . Similarly, field evaluation of moisture content did not <br /> suggest the need for a shallower screening interval, to the <br /> r ons),te geologist. During Phase II, field HNu readings were <br /> inconclusive, and were not used in determining screening <br /> }� interval. <br /> After well completion and development, water level recovered <br /> to a depth of approximately 31 feet below around surface (Mv;- <br /> �,.� 1 i . Water level was subsequently reneasuzed on July 27, 6 P11, <br /> 4-7 <br />