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Mr. Kevin Graves <br />April 28,2006 <br />Page 4 <br />After stating that the resumed monitoring of the other four existing wells "may continue to define <br />the extent of the shallow groundwater contamination", emphasis added, "The Work Plan is not <br />approved" letter went on to state that "At this time, EHD does not consider a geoprobe <br />investigation of shallow groundwater to be warranted." However, in the Request for Work Plan <br />letter EHD stated that the "work proposed should complete the investigation of the lateral . . . <br />extent of the. . . groundwater contamination." With soil sampling boreholes open to first <br />encountered groundwater, the additional effort to determine the lateral extent of any remaining <br />shallow groundwater contaminations, as requested, through grab samples of that groundwater <br />would seem to warranted! <br />In the fourth paragraph of "The Work Plan is not approved" letter, EHD seems to concur with <br />the proposed locations of the deeper screened monitoring wells as paired with existing <br />monitoring wells MW-1, MW-2, and MW-4. The paragraph summarizes the log of Thornton <br />Municipal Well. No. 2 (Attachment D), indicating that "there is sand from 25 to 60 feet below <br />grade, so the deeper portions of this sand interval are of concern." The EHD does not mention <br />that well is sealed to a depth of 70 feet, ten feet into that which on the log is shown as "blue clay <br />& shale." Nor does EHD mention that the well is cased from 0 to 135 feet, and that the well <br />screen is set from 135 to 150 feet; 160 to 185 feet; and from 225 to 235 feet. <br />EHD seems to reject the proposed 10 foot screen interval (30 to 40 feet), in that it "may be too <br />shallow and too long." Too long, perhaps. The undersigned has no objection to the EHD's <br />recommendation of a five foot long monitoring well screen interval, nor determination through <br />continuous coring, either through rotary or drive sampling to make said determinations. Though <br />not detailed in the work plan, isn't this how such a determination would be made?. As to the <br />length, for planning purposes, the log does, after all, show that the "sand and wood" sequence is <br />perhaps 35 feet thick. However, as to "too shallow", one should be very weary this close to an <br />active municipal well when punching vertical holes, as, regardless of the borehole and well <br />sealing guidelines, a vertical borehole is still a disruption of the stratigraphy and poses the risk of <br />introducing a vertical conduit of higher permeability than previously existed. For this reason, the <br />predetermination of well construction details using a cone penetrometer is rejectedposing too <br />high a risk since the small diameter of either the cone penetrometer or the Geoprobe' presents <br />the most challenging borehole to seal. In addition, it should be expected that the logged wood <br />would prevent achieving the desired depth anyway, or at best resulting in borehole advancing <br />and sealing problems. The vertical distribution in the 35 foot "sand and wood" sequence should <br />be ascertained incrementally, beginning at the depth of the deepest available nearby data. This is <br />to say the workplan implied and initial screen interval of 30 to 40 feet may be followed by a <br />screen interval of 50 to 50 feet, etc., now reduced to perhaps 35 to forty followed by 45 to 50, <br />etc. <br />H 2 OGEOL A GROUND WATER CONSULTANCY