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dliy O'1VJ <br />• 20 October 1997 <br /> AGE-NC Project No. 95-0109 <br /> Page 3 of 5 <br /> 3.2. MICROBIOLOGICAL ACTIVITY IN GROUND WATER <br /> Microbiological plate counts decreased in the ground water sample collected from MW-9 during the <br /> third quarter of 1997. General plate counts increased in MW-14, but selective degraders decreased. <br /> Nutrient concentrations generally decreased in MW-14 and MW-9, however, specific nutrients <br /> showed an increase during the past quarter. Nitrate was detected in MW-9 and MW-14 at <br /> concentrations of 0.1 ppm and 2.8 ppm, respectively. Nitrite was detected in MW-9 and MW-14 at <br /> concentrations of <0.1 ppm and 7.0 ppm, respectively. Absolute numbers of both plate counts and <br /> nutrients remain below optimum levels. <br /> Total nitrogen concentrations of 10 parts per million (ppm) to 20 ppm are preferred, and <br /> concentrations as high as 100 ppm are acceptable for maximum biodegradation. These data indicate <br /> that site conditions are less than optimal to promote biologic breakdown of the hydrocarbon <br /> contaminants. Chemical and microbiological data for ground water are summarized on Table 2 and <br /> Table 3. The laboratory report (A. Keith Kaufman - 24 September 1997) and chain-of-custody form <br /> are included in Appendix B. <br /> 3.3. PETROLEUM HYDROCARBON-IMPACTED GROUND WATER <br /> During the September 1997 sampling event, petroleum hydrocarbons were detected in ground water <br /> samples from five of the seven wells sampled. TPH-g concentrations ranged from below laboratory <br /> method detection limits to 8,600 parts per billion (ppb; reported as micrograms per liter). BTE&X <br /> were detected at concentrations as high as 260 ppb benzene (MW-14), 180 ppb toluene (MW-14), <br /> 550 ppb ethylbenzene (MW-9), and 440 ppb xylenes (MW-14). TPH-g and BTE&X were not <br /> detected in samples collected from MW-6 or MW-12 during the September 1997 sampling. <br /> Hydrocarbon concentrations decreased in four of the wells sampled, increased in one well (MW-9) <br /> and remained non-detect in two wells sampled. Charts I - 6 (Appendix C) illustrate benzene <br /> concentration verses time for monitoring wells MW-6, MW-8, MW-9, MW-10, MW-14 and EW-1. <br /> Oxygenated compounds, including MTBE, were not detected in the samples collected during the <br /> September 1997 sampling event. 1,2-Dichloroethane was detected in MW-8 and MW-9 at <br /> concentrations of 2.4 ppb and 160 ppb, respectively. Isopropylbenzene was detected in MW-8 and <br /> MW-9 at concentrations of 8.5 ppb and 140 ppb, respectively. 1,2,4-Trimethylbenzene was detected <br /> in MW-8, MW-9 and MW-14 at concentrations of 73 ppb, 760 ppb and 110 ppb, respectively. 1,3,5- <br /> Trimethylbenzene was detected in MW-8,MW-9 and MW-14 at concentrations of 6.8 ppb, 200 ppb <br /> and 20 ppb, respectively. Vinyl Acetate was detected in MW-8 at a concentration of 3.0 ppb. Other <br /> analytes included in EPA method 8260 were not detected. <br /> Analytical results of ground water samples are summarized on Tables 4 and 5. The laboratory report <br /> P <br /> Advanced GeoEnvironmental,Inc. <br />