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systems. Mixing and dilution in the aquifer as well as adsorption and adhesion in the soil substantially <br /> P � Y <br /> reduce the concentration of percolating effluent. <br /> The Hantzche and Finnemore equation is a conservative approximation of ground water nitrate-nitrogen <br /> concentration resulting from the combined effect of on-site sewage disposal systems and precipitation. <br /> The equation and method is for estimating long-term effect on ground-water quality, and is not <br /> intended for prediction of seasonal changes(Hantzsche and Finnemore, 1992). <br /> The method takes into account the development area,soil denitrification factor, rainfall recharge area, <br /> rainfall nitrate concentration, waste effluent quantity, and waste effluent nitrate concentration from on- <br /> site septic systems. The equation for calculating the project's potential to adversely impact local <br /> groundwater by increasing nitrate concentrations,also defined as long term average concentration of <br /> percolating effluent Nc, shown in Figure 3. <br /> Mass Transport Soil Properties <br /> Preliminary percolation tests at the site have revealed that the soils are permeable.The soil will allow <br /> moderate infiltration of water through the surface soils. Effluent remaining near the ground surface <br /> provides more opportunity for biologic processes to occur. In addition, soil borings at the site <br /> consistently show the presence of numerous lenses of sandy clays in the 0'to 50' depth range. Although <br /> it is not expected that the sandy clays will act as impermeable barriers, it will reduce the rate of <br /> transport and greater dispersion of nitrate. <br /> Sources of Nitrate <br /> Septic systems and dairies are significant sources of nitrate found in ground water. Farming activities <br /> using soil fertilization where sandy soils are present may also contribute to nitrate contamination, <br /> especially in shallow unconfined aquifers. The proposed project will add nitrate to the groundwater <br /> through use of an on-site septic disposal system. <br /> Although there are no data to determine groundwater gradients at the site, it is likely to follow the slope <br /> of the ground,generally from south to north. The distance between the property and a groundwater <br /> boundary(coastal hills) is short,so areas/activities that may contribute a nitrate load upgradient are <br /> limited. According to satellite photography, agrarian use is minor,and there are only 5 to 10 houses on <br /> large AR zone lots that are assumed to have on-site septic systems. <br /> The project consists of commercial warehousing,so the septic load will include bathrooms(toilets,sinks, <br /> urinals),and small breakroom area (sinks, dishwasher). Since the sewage characteristics are not the <br /> same as residential (which would include wastewater from showers, clothes washing, additional food <br /> preparation, hygiene activities),the nitrate concentration is greater. Thus, a value of 70 mg/I as N was <br /> used for the study. <br /> 51 <br />