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r _ <br /> �,;,::�_; - y, �;,.�€ ,.. � � ,F-;' E �rrot� '-� � -� '�r �%a .,_� £ =��=�-.� Ems_ -���} ..�:,�;. z�.� � :�%:: #. ,�. �•-:, <br /> � _ <br /> r; `�'r M <br /> - s _ r' <br /> x^" -r_ - :;. -fir-z r - r r 4.� �— a ..-- ---- ?', - •- = - moi-37-x- - - `r <br /> 5 <br /> the Catalytic reactor. ample a from theno ports ara on- <br /> aly2od to dotermine the hydrncabon destruction 4Lf f1CianC1or,. <br /> OPERATING PCnFe7 MAr3CF: <br /> vapor conconta'ations fron two progect sites are Shown in <br /> Figure 2, The data illustrates the broad range of vapor <br /> compositions under which the MMC is capable of operating. <br /> The top Curve shown data from an operation durin5l which the <br /> extracted vapor was in the f lamnables range. tl'ho lower <br /> flammability limit of gasoline vapors in air is ab,iut 15,000 <br /> ppm(v), or 1 .5t(v)). The. lower- curve sahous data obtained <br /> during operation of a CAR unit. At they beginning of thins <br /> project, she extracted air had a high combustible content <br /> and dilution .sir was required to prevent overheating of the <br /> catalyst. The admixture of dilution air resulted in a <br /> Mower drawdown of the hydrscarbon concentration for the <br /> first 20 days. <br /> Potential emissions to the atmosphere without control oL the <br /> vented ga. are shown in figure 3. At the 10,000 ppm(v) <br /> level and a flow rate of 100 Ctm, the emisassion% mould be <br /> almost 400 pounds per day. ' The VCP unit with supplemental <br /> l <br /> fuel would be the recommended operating node at this concen- <br /> tration of hydrocarbons. Cmissions from the VCP have been <br /> measured by numerous regulatory agencies stuch as the San <br /> Diego APCs, South Coast AQM€1, and the California Air <br /> Resources Board. In all instances the hydrocarbon do*- <br /> truCtion efficiencies have been above 99.01. Thus actual <br /> hydrocarbon emission, from the .tack are less than 1.0 <br /> lb/day. CO levels have been below 10 ppm, and NO, levels <br /> have been below 1 pprA. !.rad and sulfur have t: beton <br /> detected. <br /> At the 3,000 ppm(v) level and a flow rate of 90 Ctm, the <br /> uncontrolled emissions would be 100 lb/day. Operating a <br /> catalytic reactor at 90t destruction efficiency would redutn <br /> the emissions to 10 lb/day. It would be possible to operate <br /> the catalytic reactor at a higher destruction efficiency, <br /> thereby reducing emissions below 10 lb/day. This could be <br /> done by raising the: temperature: of the catalyst bed,. There <br /> Is a trade-off, however, between catalyst bed temperature <br /> —and-Catalyst---life.---Wo..__racam end that- <br /> be operated in a cost-effective gray to meet emission guide- <br /> lines while, at the same time, rainimixing catalyst detarl <br /> oration. At recommended operatinfj conditions the catalyst <br /> life has been found to exceed one year. <br /> 4 <br /> Emissions from operations In the CAR modes are shown in <br /> Table 1. The data are abstracted from a report subalttcd to <br />