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n <br /> Kennedy/Jenks Consultants <br /> n <br /> • Multi-parameter water quality meter(temperature, pH, specific conductance, redox potential) ' I <br /> • Turbidity meter <br /> • Flow-through cell <br /> • Nitrocellulose filters (if conducting field filtering) i l <br /> • Sample containers (laboratory-supplied) with appropriate preservatives <br /> • Additional chemical preservatives (if necessary) 9 <br /> a <br /> • Watch or stopwatch <br /> • Sample labels, pens, field logbook, or other appropriate field forms (e.g., groundwater purge <br /> and sample forms, chain-of-custody forms), and access agreements and third-party sample <br /> receipts (if warranted) <br /> • Previous purging and sampling data for monitoring wells to be sampled, including water <br /> levels, purging parameters, and laboratory analysis results. + <br /> • Monitoring well boring and construction log (including wellhead elevation survey and <br /> reference point information) e <br /> • Personnel and equipment decontamination supplies <br /> • Sample shipping and packaging supplies X11 <br /> • Personal protective equipment as specified in the Health and Safety Plan (HASP). <br /> 4.3 Typical Procedures for Monitoring Well Purging and <br /> Groundwater Sampling V <br /> 1. Pre-Puraina Data Collection and Purging Equipment Placement. Record the data and �! <br /> information collected during this procedure on a groundwater purge and sample form. Perform <br /> the following prior to groundwater sampling: <br /> a. Calibrate the multi-parameter water quality meter, prior to beginning sampling and as <br /> necessary based on field conditions, in accordance with the instructions in the <br /> manufacturer's operation manual. Note that it may be appropriate to keep a written log of <br /> the calibration procedures and an instrument maintenance with the instrument. <br /> b. Examine the monitoring well to be sampled and associated protective surface enclosure for <br /> any structural damage, poorly fitting caps, and leaks into the inner casing. If notable <br /> conditions exist, they should be recorded on the sampling log for the well so that any <br /> necessary follow-up corrective actions can be planned and implemented. <br /> c. Record an initial measurement of the depth to water. Calculate the volume of water in the tJ <br /> well casing if wetted-casing-volume-based purging is to be used to remove the so-called <br /> "stagnant water" from the well prior to sampling. The volume of water in the wetted well J <br /> casing should be calculated using the formula: V = (7E r2) x L where r is one half of the inner <br /> diameter of the well casing/screen and L is the length of wetted casing/screen (calculated by , <br /> subtracting the depth to water from the total well depth). Total well depth should not be J <br /> measured at the start of a sampling event (due to the potential to cause turbidity). Measure <br /> the total well depth after sample collection. Note that some regulatory agencies require that <br /> the calculated "stagnant water" volume include the water contained in the pores space of the 1 JI <br /> Hydrogeo/ogic Investigation and Groundwater Sampling and Analysis Work Plan SOG 4 <br /> Sutter Home Lodi Winery, Lodi, California Page 2 of 7 <br /> gVsy=pWminyab1060865005 b S%1"Yftw plenleppVn XWWpa_s*W gxsamprevO <br />