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I <br />' 18 July 2002 <br /> i AGE-NC Project No 96-0254 <br />' Page 15 of 17 <br /> 6 2 4 Duration <br />' Cleanup durations for in-situ bioremediation will vary,depending upon specific site characteristics <br /> However,an 18 to 36 month treatment penod is commonly achievable Since dissolved hydrocarbon <br /> concentrations at the site are moderate to high, a cleanup period of 24 to 36 months may be <br /> projected <br /> I <br /> 6 2 5 Cost <br /> Bioremediation of ground water can be a very cost-effective method of treatment With little on-site <br /> equipment required beyond the initial inoculation, the cost for in-situ bioremediation at the site <br /> would be between$40,000 and$60,000 However,monitoring will vary depending upon regulatory <br /> requirements, which could significantly increase the total cost of the project <br /> Typical costs for monthly monitoring of an in-situ bioremediation system, in addition to standard <br /> quarterly sampling, would be approximately $1,500 per month Based on a one and one-half year <br /> treatment period, the total cost for in-situ bioremediation at the site would be between$70,000 and <br />�. $95,000 <br /> I6 3 MONITORED NATURAL ATTENUATION <br /> Natural attenuation, or passive bioremediation, is a remedial alternative that relies on natural <br /> processes to degrade hydrocarbons Biodegradation is the most important natural attenuation <br /> mechanism No additional bacteria or nutrients are added to the soil or ground water Essential <br /> nutrients required for biodegradation are commonly naturally present in the subsurface However, <br /> where high concentrations of hydrocarbons are present, nutrients may be consumed before <br /> hydrocarbon remediation is complete <br /> Oxygen depletion in the subsurface is a characteristic of biodegradation The core of a contaminant <br /> plume is typically under anaerobic conditions and only the margins are aerobic Therefore, even <br /> though anaerobic biodegradation is much slower than aerobic biodegradation, anaerobic processes <br /> may dominate the degradation of contaminants Groundwater movement will generally assist in the <br /> transport of nutrients in the saturated zone <br /> Natural attenuation is normally used where low concentrations of hydrocarbons are present, <br /> following completion of another form of remediation or in an area where no domestic or irrigation <br /> Iwells are threatened Concentrations of hydrocarbons have remained relatively stable in monitoring <br /> . wells MW-1 B and MW-4 over time,continued ground water monitoring would be required to show <br /> decreasing hydrocarbon concentrations <br /> Advanced CevT;nvirvnmental,Inc <br />