Laserfiche WebLink
dissolved petroleum hydrocarbons in the sandy portion of the aquifer will travel 4.69 feet/year. <br /> Calculations are presented in Appendix V. At this time, it is uncertain the extent of dissolved <br /> petroleum hydrocarbons in the plume. Further investigation is required. However, the rate of <br /> flow in the sandy portion of the aquifer is not significant. These flow rates may explain the <br /> &W limited size of the plume since the source of the contaminants (the former gasoline USTs) were <br /> removed in 1986. <br /> L <br /> 6.0 INTRINSIC BIOREMEDIATION OF GROUNDWATER <br /> �_J Discussion <br /> LM <br /> Several detailed field studies have been performed examining indicators of intrinsic <br /> bioremediation and identify factors which significantly effect the rate and extent of <br /> bioremediation (Buscheck and others, 1993; McAllister and Chiang, 1994; Borden and others, <br /> 1995; Buscheck and Alcantar, 1995). Through these studies and on-going research on the <br /> L factors which control biodegradation, it is now understood that dissolved petroleum <br /> hydrocarbons in groundwater will biodegrade, without artificial enhancement, due to the <br /> presence of naturally occurring (indigenous) microorganisms. Technical protocols for <br /> implementing and monitoring intrinsic bioremediation studies in groundwater have been <br /> developed by the US Air Force and Chevron Corporation. <br /> Intrinsic bioremediation in brief, is the use of indigenous microorganisms to degrade <br /> contaminants which have been released into the subsurface. The biodegradation of the <br /> contaminants is essentially an oxidation-reduction (redox) reaction where the hydrocarbon is <br /> oxidized (donates an electron) and an electron acceptor (i.e. oxygen) is reduced (accepts <br /> electrons). There are several compounds that can serve as electron acceptors including <br /> oxygen, nitrate, iron oxides, sulfate, water, and carbon dioxide (Borden and others, 1995). <br /> Aerobic microorganisms use oxygen as the electron acceptors. Anaerobic microorganisms use <br /> other compounds such as nitrate, iron oxides (ferric iron), and sulfate as electron acceptors. <br /> Oxygen is the most preferred electron acceptor in groundwater because microorganisms gain <br /> more energy from these reactions, however, this process usually results in the depletion of <br /> oxygen with an increase in carbon dioxide in the subsurface. Therefore low concentrations of <br /> �. dissolved oxygen and corresponding high concentrations of carbon dioxide within hydrocarbon <br /> plume indicate biodegradation is taking place (Borden and others, 1995). <br /> i <br /> L <br /> w:195122TIumerpt 12 <br /> • <br /> Sion <br /> L <br />