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r <br />r <br />r <br />r <br />r <br />�- <br />�. <br />�. <br />� <br />ADaPT Enr;ineerinp, I�n_ <br />approximately 8 feet bgs. Below 8 feet bgs, the soil became firtn to hard moist yray to dark gray <br />day with trace sand which was irterpreted to be glacial tlll or'hardpan". The glaaal till deposit <br />extended to the full-explored depth of 28.5 feet. Gladal 811 is a glacially overcansolidated deposit, <br />which was compressed by the weight of thousands of feet of gladal ice. Accordingly, the dll and <br />all soil units deposited stra8graphically below the till are very derue and relativey incompressible. <br />Dense to very dense or hard soil conditions were encountered for the full depth of the test boring <br />below 12-feet bgs. <br />5.3 Groundwater Conditlons <br />Free water was not encountered in the boring during drilling. However, very moist to wet day soil <br />was encountered in the boring betwcen 8 and 10 feet. The adjacent BP Station monitoring wells <br />indicate that groundwater is approximately 4 to 10 feet below ground surtace. It should be <br />recociized that groundwater levels could fluctuate due to factors such as seasonal changes, <br />precipitation or future site utilization. <br />Although groundwater flow direction is difficult to predict without the installation of at ieast three <br />monitoring wells that measure water levels over time, an estimate of possible near-surface <br />groundwater flow direction is provided to help evaluate potential on-site and off-site contaminant <br />impacts. Groundwater flow direction is the path along which dissolved contaminants might <br />migrate if present in groundwater supplies. Typically, in this region, ttie near-surtace groundwater <br />flow direction generally follows topography. The subject area sbpes down to the west and so <br />near-surface groundwater flow direction likely follows the tupogr^.phy and moves toward the west. <br />Variations in the assumed flow direction may exist that would remain uncharacterized without <br />performing a subsurface exploration program with groundwater monitoring wells, which is beyond <br />the Phase I scope of work. <br />1 Based on the review of Washington State Department of Ecology LUST file for the adjacent <br />gasoline station the groundwater is reportedly flowing towards the west-northwest. According to <br />the file the depth to groundwater is approximately 4 feet to 5 teet in the well to the east of the <br />lease area. <br />� 5.4 Drinking Water Suppifes and Water Wells <br />� The host parcel and surrounding area obtain their public drinking water supply from the Ciry of <br />Everett Public Works Department. According to staff personne� for the Public Works Department, <br />the PWD obtains its water supply from Spada Lake Reservofr bcated at the headwaters of the <br />� Sultan River approximately 30 miles east of Everett. Based on the separation distance, it is highly <br />unlikely this drinking water supply would be fnfluenced by the host parcel. <br />' A review of water well reports at the Washington Department of Ecology (Ecology) Northwest <br />Regional Office in Bellevue, Washington revealed approximately four domesdc drinking water <br />wells located within one mile of the subject site. These wells appear to be over one-quarter mile <br />_ away from the host parcel and appear unlikely to be influenced by the host parcel. <br />6.0 HISTORICAL USE INFORMATION <br />This section is divided into two subsections. The first subsection (Section 6.1) summarizes the <br />various historical sources that were consulted. The second subsectlon (Section 6.2) is a decade <br />by decade discussion oF the historical uses of the host parcel and immediate surrounding area. <br />VoiceSVeam•Masonlc Center �� 5� � <br />ADaPT Projecl No. WA00�4147-7 � S <br />