Laserfiche WebLink
GROUND WATER INVESTIGATION WORK PLAN <br />BULK TERMINALS SITE, PORT OF STOCKTON, STOCKTON, CALIFORNIA <br /> <br />below. Water sample containers will be sealed, labeled, and placed in a cooler containing ice <br />immediately after collection. The label will identify the boring number, upper depth of the <br />sample interval, date and time of sample collection, and sampler's initials. The samples will be <br />transported to the designated state-certified laboratory following standard chain-of-custody <br />protocols. Samples to be analyzed for dissolved metals concentrations will be filtered at the <br />laboratory using a 0.45 µin filter prior to sample preservation. <br />3.1.2.6 Boring Completion <br />Upon completion of sampling and data collection activities, the borings will be tremied from the <br />bottom to the surface using a mixture of neat cement and bentonite clay. The top of the boring <br />will be finished in a manner similar to surrounding materials. <br />A licensed surveyor will locate each boring relative to mean sea level elevation. The boring <br />locations will also be located horizontally within the NAD 23 coordinate system using the <br />Global Positioning System (GPS). <br />Soil materials generated from the borings, and water and wastewater generated from <br />investigation and decontamination activities will be placed in a 55-gallon Department of <br />Transportation (DOT) drum, labeled appropriately, and stored on-site pending future disposal. <br />Results of soil and ground water sample analyses may be used to identify appropriate disposal <br />facilities. <br />3.1.2.7 Existing Monitor Well Sampling <br />Ground water samples will be collected from wells MW-1 through MW-4 to supplement <br />ground water data from the screening-level sampling. At each well, depth to water and total <br />well depth will be measured to the nearest 0.01 foot with an electronic water-level indicator. <br />Following depth-to-water measurements, a minimum of three casing volumes of ground water <br />will be purged using disposable bailers or a peristaltic pump. Temperature, pH, conductivity, <br />and dissolved oxygen content (DO) of the purged water will be monitored in the field during <br />well purging. Purging will continue until water parameters stabilize to within 10 percent of <br />successive measurements. <br />Samples will be collected after the water level has recovered to at least 80 percent of the original <br />volume in the well. If the well is purged dry, additional purging will not be performed and <br />samples will be collected after the water level has recovered to 80 percent of the original volume <br />in the well. Ground water samples will be collected into laboratory prepared bottles using a <br />disposable bailer or peristaltic pump. The bottles will promptly sealed, labeled, and placed in a <br />chest containing ice pending transportation to the analytical laboratory. Samples to be analyzed <br />for dissolved metals concentrations will be filtered at the laboratory using a 0.45 µm filter prior <br />to sample preservation. <br />July 2005 Page 12 Environmental Risk Services Corp.