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FYREZYME MECHANISM OF ACTION <br /> Soil and its complex structure, microbial colonies, and biochemical makeup can accept and degrade into non- <br /> toxic forms, a wide variety of pollutants. There exists in nature microbial forms (bacteria, yeast, molds, etc.) <br /> which can biodegrade most agents which are noxious to the environment. These microbial agents have the <br /> capability to produce enzymes which lead to the breakdown (mineralization) of the polluting agents, <br /> transforming them into energy sources for the microbe's own metabolic use. This process continues until all <br /> that remains of the contaminant are CO2, H2O, and biomass (fatty acids which are used for energy source by <br /> other microorganisms). The biodegredation of contaminants can be accomplished both in oxygen-rich <br /> (aerobic) and in oxygen-poor (anaerobic) environments. The aerobic mineralization of contaminants is much <br /> faster and more complete than the anaerobic process. Both aerobic and anaerobic treatment may be necessan- <br /> in certain circumstances. <br /> At sites contaminated with petroleum product, a certain percentage of the overall bacterial population is <br /> capable of utilizing the petroleum products as a source for energy and growth. Having a readily available <br /> source of such preferred food, the petroleum-consuming bacteria are favored in the biological chain and <br /> increase in number at the expense of bacteria without that special capability. After the petroleum is eliminated <br /> from the soil (or water), the bacterial population returns to the same ratios present prior to the addition of a <br /> contaminant to their environment. <br /> There are multiple factors which determine the speed and completion of breakdown of contaminants in both <br /> soil and water. In this discussion, we shall consider the action of soil bacteria on petroleum contaminants. The <br /> limiting biological_ factors include, among others, <br /> -the type, concentration, and distribution of petroleum product <br /> (addressed in separate communication) <br /> -the presence of bacteria capable of digesting petroleum <br /> -the availability of energy sources for bacterial metabolism/gcwth <br /> -the availability of oxygen in sufficient quantity to support metabolism <br /> -the ability of bacteria to come into contact with the petroleum <br /> -the ability of the enhancing agent to come into contact with bacteria <br /> and petroleum <br /> -soil moisture level and pH(acidity or alkalinity) <br /> -temperature of soil environment <br /> Presence of Bacteria Capable of Digesting Petroleum: <br /> Even in the absence of recognized oil spills, there are naturally-occurring soil bacteria which are capable of <br /> altering their metabolic activities to allow them to digest petroleum. Their numbers are very small, but will <br /> increase readily in the presence of a petroleum-rich environment. Fy-reZyme preferentially increases <br /> petroleum-consuming bacteria by several orders of magnitude. By Darwinian selection, their growth is favored <br /> and their overall percentage within the microbial population increases dramatically. <br />