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EM 1110-1-4001 <br /> 3 Jun 02 <br /> • c Estimating the Impact ofD ffusion Limitations on Remediation Timeframes <br /> (1) By measuring rebound rates and using a simple analytical model (Brusseau 1996)some <br /> practitioners are able to estimate the impact of rate-limited mass transport on remediation timeframes <br /> G� t Praxis Environmental Technologies,Inc developer of the PneulogTM tool,reports that mass transfer <br /> �t"� �` f constraints,order-of-magnitude total mass,and time to cleanup can be estimated from historical <br /> concentration data and rebound test data Figure 9-2 shows data collected using a PneulogTM device to <br /> vertically profile extracted concentrations and flow rates in a single SVE well during a rebound test SVE <br /> �3. was performed at this site for 12 days,then paused for four days,and then reinitiated at the same flow rates <br /> lr� as before The data show the characteristic rebound in extracted vapor concentrations that is seen in most <br /> SVE systems At this site,the rebound in TCE concentration is presumably due to diffusion from a less <br /> wpermeable zone into the pathways that transmit most of the air to the extraction well After the pause,a <br /> rebound in the extracted vapor concentration of almost 10 percent was observed <br /> (2) Figure 9-2 also includes a plot of the results of Brusseau's model,with best-fit parameters, and <br /> displays a close match with the measured concentration decay and rebound The model has been developed <br /> in the academic literature(Brusseau 1996)but is used infrequently in field practice because the proper data <br /> are not collected or practitioners are not famihar with the model <br /> The bask simplifying assumptions in the model are <br /> • soils are categorized as two-domain,i e,permeable to air flow(mobile)or not(immobile), and <br /> • the early flushing rate of the mobile zone by clean air is rapid enough to justify averaging the <br /> contaminant concentration in the mobile zone <br /> (3) Typical SVE flow rates flush the mobile zone with clean air every few days justifying the <br /> averaging assumption Most sites readily meet the conceptual model of mobile and immobile zones for air <br /> movement during SVE A third category of low flow zones(e g, silts)can be added if sufficient site data <br /> exist Air moves through the mobile soils and contaminants must diffuse out of immobile zones before <br /> being extracted The form of the equation describing the vapor concentration in the mobile zone(assumed <br /> equal to the extracted concentration)is roughly <br /> Cmobile is a function of [Contribution of Mobile Zone]+ [Contribution of Immobile Zone] <br /> or <br /> {'r rlt r_r <br /> C'n"b e = 10 8 +Oze ) (9-1) <br /> where <br /> 01 =an advective decay constant <br /> Oz =a diffusive decay constant <br /> ri =a function of air residence time within the soil pores <br /> r2 =a function of the compound's diffusivity in the rate-limiting soil type <br /> t= elapsed soil venting time <br /> 9-11 <br />