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IV. CONCLUSIONS AND RECOMMENDATIONS <br /> The data presented above gives an approximate estimate of what is occurring at the subject <br /> facility with regard to nitrogen production and crop uptake. There are numerous factors involved <br /> in adequately assessing and correlating crop needs and uptake of available nitrogen. From the <br /> results of the balance equation, the amount of nitrogen produced by the dairy operation is <br /> approximately 82% of the nitrogen needed for optimum crop growth. When large numbers are <br /> formulated to assess nitrogen produced vs. nitrogen required, the margin of error can be±10%. <br /> Therefore, it is recommended that sampling and analysis be performed on the 1.) Wastes applied, <br /> 2.) Cropland soil and 3.) Tissue samples of the crops to check for N excess. By analysis of these <br /> different parameters, it can best be determined which form of nutrient(solid vs. liquid) to apply to <br /> _ a particular field. Additionally, the Estimated Nitrogen Release (ENR) must be taken into <br /> consideration when determining nutrient application quantities. <br /> The procedures for determining crop nutritional needs, particularly nitrogen, without overloading <br /> the cropland can be a complex process. In an effort to simplify the information required to make <br /> best management decisions for optimum crop growth and nutrient utilization, we have provided a <br /> Manure Analysis Reference Guide attached with this report. This Guide is published by A & L <br /> Agricultural Laboratories and provides one of the best sources of information to determine crop <br /> nutrient utilization from animal wastes. The suitable rate of solid and liquid applications is <br /> determined by the ability of the soil and crop combination to immobilize and utilize the nutrients <br /> in the applied manure, which is detailed on the Worksheets found in this Guide. <br /> In our opinion, the actual dairy site is the primary area of concern with respect to nitrate/nitrogen <br /> loading, followed by the cropland. The calculated nitrogen contribution from the on-site sewage <br /> disposal systems is comparatively insignificant, especially when the surrounding land use low <br /> density factor is considered. <br /> _ One of the most significant nitrate mitigating factors discovered from this investigation is the <br /> process known as denitrification: The microbial reduction of nitrate to nitrogen gas and nitrous <br /> oxide. This process is one of the explanations for the relatively low levels of nitrate found in the <br /> _ cropland soils and underlying groundwater. Due to the high clay content cropland soils, the <br /> denitrification process prevails in the subsurface anaerobic conditions within the microsite pore <br /> spaces of the clay. <br /> Caution must be exercised when irrigating cropland. Tailwater must not be allowed to enter any <br /> of the canals or ditches surrounding the cropland. The infiltration and permeability of all nutrient <br /> .. application acreage is comparatively slow and runoff can occur readily. In addition, wastes must <br /> be managed at the south end of the corral area so that no solids or liquids enter Nagler Draw. <br /> From the analysis of the groundwater, the gradient and estimated directional flow, nitrate impact <br /> to downgradient domestic wells from the subject dairy exclusively, appears remote. <br /> An increase in animal units may be made, up and above the numbers used. However, if an <br /> increase in AUs is proposed, an analysis must be made to quantify the additional nitrogen <br /> production, in combination with new waste management techniques (e.g., freestall flush system). <br /> 8 <br /> Vaffey Ag Pcsearck <br />