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' Former Manna Pro Site Page 4 <br /> Quarteily Groundwater Monitoting Repoit <br /> &Monitoring Well Construction <br /> Ptoject No 207 2 <br /> June 2, 2000 <br />' While drilling, with hollow stem auger tools, all soil cuttings were placed in <br /> D O T approved, steel 55 gallon drums for temporary storage pending profiling <br />' and proper disposal The drilling mud and the entrained soil cuttings were also <br /> temporarily stored in drums <br />' 2 1.2 In Situ Sample Collection Procedures <br /> During the hollow stein auger boring process soil samples were collected for <br /> geological and analytical evaluation at five foot intervals using a 2 0 inch <br />' diameter (i d ) California split spoon sampler with the sample contained in 2 by <br /> 6 inch stainless steel liners The sampler was driven up to 18 inches into the <br /> native soil using the 140 pound hammer mounted on the drill rig The blow <br />' count was recorded for each sample collected All soil samples were sealed with <br /> aluminum foil, capped, labeled and placed in a cooler at 4c' Celsius for transport <br /> to the laboratory following Chain of Custody protocol <br /> I <br /> During the mud rotary drilling process, a SimulProbe sampling tool was used to I <br />' obtain soil and groundwater samples The SzmulProbe is a direct push tool <br /> which is hammered into the base of the soil boring after the drill stem has been <br /> temporarily removed from the hole The device is capable of retrieving up to 18 <br /> of soil in a modified split spoon sampling device The sample is contained in <br /> vertical inches of soil in three 6 inch by 2 75 inch diameter stainless steel sample <br /> sleeves In addition, a screen with a retractable shield allows up to two liters of <br />' water to enter the sampling device While lowering the sampling tool to the <br /> bottom of the boring, a large rubber condom is used to keep drilling mud from <br /> entering the sample containment spaces In this case SimulProbe samples were <br />' collected from the intervals at 55 feet, 69 feet and 96 feet No water sample was <br /> retrieved at the 55 foot level, but a soil sample was obtained Both soil and <br /> groundwater samples were obtained at the 69 and 96 foot levels <br /> 1 <br /> Boring logs of soils encountered in the boring were kept by a registered geologist <br />' (see Appendix C) Recorded in these logs were notes on sampling intervals, <br /> boring locations and sediments intersected by the boring Not all soil samples <br /> collected were submitted for laboratory analysis Accordingly, a field screening <br />' procedure was used to select those samples which were tested Special attention <br /> was paid to sediment type, color, grain size, sorting, odor and the readings above <br /> background on an organic vapor meter (OVM) The OVM is a field portable <br />' photo ionization detector that uses a 10 2 eV lamp to detect compounds with <br /> ionization potential below 10 2 eV (hydrocarbon range) In addition to the on- <br /> site laboratory, selected samples were submitted for normal laboratory analysis <br /> • <br />' 2937 Veneman Ave,#B240 Geo-Phase Environmental Inc Phone (209) 569-0293 <br /> Modesto, CA 95356 Fax (209) 569-0293 <br />