Laserfiche WebLink
Firstuarter 2001 Ground Wa <br /> Q ter Monitoring Report <br /> Cleanea and Abatement Order No 5-00-707 EAI Project No 1232 <br /> 2 0 FIELD INVESTIGATION <br /> 21 Ground Water Elevation Survey <br /> On March 27, 2001, all new well casing elevations (see Section 1 1 2) were surveyed to the <br /> established referenced datum point for the project <br /> ' 2.2 Ground Water Sampling <br /> On March 27, 2001, prior to purging or sampling activities, depth measurements to fluid levels <br /> ' were obtained by EAI from all monitoring wells associated with the Wards (MW-1 through <br /> MW-7) and Unocal (MW-10 through MW-25D) sites Depth measurements were obtained <br /> using an interface probe accurate to 0 01 foot (see Table 2) <br /> No free-product was detected in any of the wells The water level measurement for each <br /> well <br /> was converted to mean sea level (MSL) datum by subtracting the measured water level for each <br /> ' well from its respective "top of well casing elevation" datum (see Table 2) <br /> On March 27 and 28, 2001, ground water samples were collected by EAI from all ground water <br /> monitoring wells associated with the Wards and Unocal sites Prior to sampling, the wells were <br /> purged using a Grundfos MP-I submersible pump Temperature, conductivity, pH, and <br /> turbidity were recorded to evaluate the effectiveness of purging activities (see Appendix A) <br /> The wells were sampled in the order that purging activities were completed <br /> As requested by the RWQCB, all wells associated with the Wards and Unocal sites were to be <br /> sampled using a point source bailer Mr Marty Hartzell with the RWQCB was present during <br /> sampling of well MW-7, the first well sampled during this sampling period Well MW-7 was <br /> sampled using a point source bailer After reviewing the sampling procedure in the field with <br /> Mr Hartzell, it was determined that sampling using disposable bailers was as representative as <br /> the point source bailers, and therefore, all remaining water samples were obtained from dust <br /> below the water surface using Voss Technologies disposable bottom bailers equipped with <br /> ' volatile organic compound sampling tips Use of these bailers precludes the potential for cross- <br /> contamination <br />' Each water sample was sealed in three 40-milliliter volatile organic analysis (VOA) vials with <br /> Teflon septa lined lids The VOA vials were completely filled so that no head space existed <br /> between the sample and the lids The samples were labeled with the sample point <br /> identification, preservative added, if any, date, time, and EAI project number, and immediately <br /> placed into a chilled ice chest The samples were kept chilled until delivered to the laboratory <br /> for analytical testing All samples were logged on a chain of custody record form (see <br /> Appendix B) <br /> 0HL1 MM0171 4 <br />' ENVIRONMENTAL AUDIT, INC <br />