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I <br /> obtain these essential materials elsewhere. To preclude <br /> nutrient deficiencies, macro- and micro-nutrients will be � <br /> carefully monitored and supplied appropriately via a <br /> metering pump system. <br /> In addition to the above, two interesting processes can, <br /> and probably most often do , occur in the degradation of <br /> petroleum hydrocarbons . These are sparing and co- <br /> oxidation. Acetate, an intermediate product in hydrocarbon <br /> biodegradation, has been found to reduce the utilization of <br /> hexadecane . The basis for this sparing effect is not well <br /> defined, but it certainly occurs for other hydrocarbons , as <br /> well . Co-oxidation is a process in which compounds which , <br /> otherwise would not be degraded can be attacked by enzymes <br /> due to the abilities of: the individual microorganisms <br /> producing the enzymes to utilize other hydrocarbons within <br /> the petroleum mixture. The complexities of petroleum <br /> compounds provide an excellent chemical environment in <br /> which co-oxidation can occur , and many complex branched and <br /> cyclic hydrocarbons are. degraded as a result . It has been <br /> found, for instance, that the degradation of hydrocarbons <br /> within a gasoline mixture occur at a rate different from <br /> the degradation of individual compounds comprising the <br /> mixture . Phenomena such as these do not alter the <br /> metabolic pathways of degradation, but determine whether <br /> the enzymes necessary for metabolic attack on a particular <br /> hydrocarbon are active, . or even produced. Metabolic rates <br /> of system biomass will be monitored, as necessary , to <br /> ensure the system is sufficiently active to remediate <br /> contaminants in a timely manner . <br /> Following treatment , remediated water will be discharged to <br /> Lfhe <br /> sanitary sewer under the authority of a permit issued <br /> or this purpose. Fuel hydrocarbons sorbed onto, soil <br /> particles in the saturated zone will also be remediated <br /> using this technology through the dynamics of equilibrium <br /> stoichiometry. A schematic of the biareactor system <br /> proposed for the site will be submitted by June 1, 1994 . <br /> In order to provide contaminated water to the bioreactor <br /> system, EPM proposes to construct a 4-inch diameter <br /> groundwater extraction well approximately 10 feet north of <br /> the northwest corner of the on-site building. It is <br /> proposed that the well penetrate the water table 3 to 4 <br /> feet in order to target the LNAPL contaminants of concern <br /> at the site and avoid the extraction of large volumes of <br /> uncontaminated water from deeper, more permeable soils. The <br /> rate of water extraction is expected to be no less than 2 .5 <br /> gallons per minute. . . a rate sufficient to create a draw <br /> �' Page 10 <br />