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I <br /> 2- Check and record the condition of the wellhead for damage or tampering. If ground conditions warrant, lay out the <br /> sheeting to encircle the wellhead to minimize the likelihood of contamination of sampling or purging equipment. Place <br /> equipment on the sheeting. Record any remarks on groundwater sample log. <br /> • 3. Unlock the wellhead. Before proceeding, record location, time, date and other information in the groundwater sampling <br /> log, <br /> 4. Remove wellhead and crack open the casing plug cap. <br /> 5. Monitor the headspace for VOCs with a Photo ionization detector(PID) or Flame ionization detector(FID) supplied with <br /> the proper lamp,and record in the sampling log. <br /> 6. Measure depth to water to nearest 0.01 feet. Measure it twice for confirmation. Measurements should be within 0.01 feet <br /> or remeasure. DO NOT MEASURE TOTAL DEPTH AT THIS TIME. <br /> 7. Check the previous sample log for well depth. Use that information to calculate the volume of the water in the monitoring <br /> well or the volume of one casing. Record this information on the groundwater-sampling log. <br /> Purging and Sampling Activities <br /> Tubing will be dedicated to each well (both silicone and poly). it will either remain in the hole at the appropriate depth (if <br /> disconnected from a peristaltic pump at the surface) or pulled out with the non-dedicated submersible pump, disconnected, <br /> reinserted and hung back in the hole at the appropriate depth, or coiled and stored in a baggie labeled with site and well I.D.for <br /> the next sampling event. If left in the hole,tubing should be marked(Sharpie indelible)to indicate proper well insertion depth. <br /> &. Non-dedicated submersible pump system — Slowly lower the pump and tubing down into the monitoring well until the <br /> location of the pump intake is set at a pre-determined location within the screen interval. Refer to the construction <br /> diagram to determine the depth and length of the screen interval. Measure the depth of the pump intake while lowering the <br /> pump into location. Record pump depth in the sampling log. <br /> 9. Dedicated submersible pump system (tubing an pump already installed) — Refer to the available monitoring well <br /> information and record on the.sampling log the depth of the dedicated submersible pump, or tubing (in the case of a <br /> peristaltic pump), hung in the well . <br /> 10.Measure the water level and record. Leaving probe in the monitoring well at depth. <br /> 11.Con nett the discharge line from the pump to a FTC. The discharge line from the cell must be directed to a container to <br /> contain the purge water. <br /> I2. Start pumping the well at a flow rate of less than 500m1/minute). Check the water level. Maintain a steady flow rate <br /> • while maintaining a drawdown of less than 0.33 feet. If drawdown is greater than 0.33 feet decrease the flow rate. 0.33 <br /> feet is a recommended goal to help guide with the flow rate adjustment, but is not mandatory. This goat may be difficult <br /> to achieve under some circumstances and may require adjustment based on site-specific conditions, and personal <br /> experience. <br /> 13. Measure the discharge rate of the pump with a graduated cylinder (1 Liter) with a watch that has a second hand. Also, <br /> measure the water level and record both flow rate and water level on the sampling log. Continue purging, monitor and <br /> record water level water-quality parameters, and pump rates every three to five minutes during purging. Pumping rates <br /> should be kept at a constant minimal flow rate to ensure minimal drawdown in the monitoring well. <br /> 14. Durin g the purging, one purging volume should be purged prior to recording the water quality parameters. Eliminate the <br /> formation of air bubbles in the tubing by rectifying leaks between spliced tubing's. Then monitor and record every three <br /> to five minutes. The stabilization criterion is based on three successive readings of the parameters;The following are the <br /> criteria which must be used: <br /> Parameter Stabilization Criteria j <br /> pH ± 0.1 pH units <br /> Specific Conductance ± 3% in S/cm <br /> Oxidation-Reduction Potential ± <br /> 10 millvolts <br /> Turbidity ± 10%NTUs(when turbidity is greater than 10 NTUs <br /> Dissolved Oxygen ± 0.3 ug/L <br /> 15. If a stabilized drawdown can't be maintained at 0.33 ft.and the water level is approaching the top of the screened interval, <br /> reduce the flow rate or turn the pump off for 15 minutes and allow recovery. Under no circumstances should the well be <br /> pumped dry or pumped below the top of the screen. After 15 minutes begin pumping at a lower flow rate, if the <br /> drawdown approaches the well screen interval again turn off the pump and allow recovery. Attempt low flow purge again. <br /> Allow recovery and proceed with sampling. This information must be noted in the groundwater-sampling log. <br /> 16. R educe the pumping rate to 100ml/minute for sampling in order to minimize disturbance of the water column. Do not go <br /> • below I00ml/minute as this may cause the pump to stall. Disconnect the tubing at the FTC. Samples should be collected <br /> directly from the discharge port of the pump tubing prior to passing through the FTC. In other words, disconnect the <br /> tubing from the FTC intake and sample at that point, not after the FTC. All VOC sample containers should be filled with <br /> minimal turbulence by allowing the groundwater to flow from the tubing gently down the inside of the container, forming <br /> 2 <br />