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Nitrate Loading Study Irerracon Roque Property ■Victor, California July 6, 2018 ■Terracon Project No. NA187032 NITRATE LOADING STUDY ROQUE PROPERTY (APN 051-100-12) 17386 N. CHERRYWOOD STREET VICTOR, SAN JOAQUIN COUNTY, CALIFORNIA OUR PROJECT NUMBER: NA187032 Our office was contacted by Ms. Jennifer Roque, site owner, to conduct a Nitrate Loading Study (NLS) for the property at 17386 N. Cherrywood Street, Victor, San Joaquin County, California. The formatting of this report has been designed to follow, to the greatest degree possible, San Joaquin County Environmental Health Department (EHD) Nitrate Loading Study Requirements Checklist, dated July 14, 2003. The site is located on an approximately 0.13-acre parcel`Mproved with;a two bedroom residence and a septic system. A two bedroom mobile home and an additional on-site septic system is proposed to be located on the eastern portion of the site. Because of concern regarding nitrate leaching into groundwater from septic systems, a nitrate loading analysis is required by the EHD for the proposed development to determine the potential concentration of percolating effluent and rain fall over the long term. Where percolating effluent leaches into the ground, groundwater quality may be impacted to some degree should the effluent reach groundwater. The method utilized for the nitrate loading analysis is based on a simple mass balance formula, discussed in a published article by Hantzsche and Finnemore (1992), which provides a convenient and simplified method to estimate long-term groundwater nitrate impacts on an area- wide basis. Hantzsche and Finnemore found that over a long period of time, water quality in the upper saturated groundwater zone closely approximates the quality of percolating recharge waters. They believe that their method is a good planning tool and provides useful information to planners and local officials but with some real limitations. In their article published in Ground Water, Hantzsche and Finnemore mention that "...the equation ignores dispersion, lateral flow, and mixing with groundwater flow from up-gradient areas. These processes would generally contribute to additional reduction of nitrate-nitrogen concentrations in groundwater to the extent that the nitrate-nitrogen concentration of groundwater flow from up-gradient areas is lower." The Hantzsche and Finnemore approach is "...a conservative (worst case)first approximation of groundwater nitrate-nitrogen concentration resulting from the combined effect of on-site sewage disposal systems and precipitation. This (the equation and approach) is for estimation of long- term effect(i.e., over years)on groundwater quality, and is not intended for prediction of seasonal changes" (Hantzsche and Finnemore, 1992). Responsive■ Resourceful ■ Reliable 2