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( KLE/NF-ELDER <br /> B14M ft p'..fth,SpluMoni. <br /> • 11. As shown in Table 8, nitrate-nitrogen was detected in the groundwater samples from <br /> MW-2 and MW-5 at concentrations of 58.9 mg/I and 49.7 mg/I, respectively. Well MW- <br /> 2 is located at approximately the southeast corner of the nursery property. Both <br /> concentrations are in excess of the State of California Maximum Contaminant Level <br /> [MCL] for nitrate-nitrogen of 10 mg/I in drinking water as expressed in §64431 of Title <br /> 22 of the California Code of Regulations [CCR]. These results are significant for two <br /> reasons. First, because this is the third of four groundwater monitoring events that <br /> revealed nitrate-nitrogen in the monitoring well upslope (upgradient) of the nursery <br /> above the MCL. Secondly, the concentration of the nitrate-nitrogen in this upgradient <br /> well (MW-2) is significantly higher than the concentration in the downgradient well (MW- <br /> 5). <br /> 12. Based on the limited investigation and monitoring data obtained, it is unknown if the <br /> shallow perched water is continuous between MW-2 and MW-5. Based on the limited <br /> investigation and monitoring data obtained, it is unknown why the concentrations <br /> increased in the upslope well (MW-2) while the concentration decreased in MW-5 <br /> (downgradient well) between the March 1998 and present. Especially since Norman's <br /> Nursery began irrigating on April 20, 1998 and has irrigated all but three days since May <br /> 16, 1998. It is unknown what the source of the perched water and nitrate-nitrogen is, <br /> that existed upslope of the nursery. Natural recharge, springs, vernal pools and the <br /> cattle grazing may be the explanations. Furthermore, the cause of the decrease and/or <br /> dilution of the nitrate-nitrogen in the groundwater near MW-5 are also unknown. <br /> 13. Total annual precipitation near the site has recently been [as high as] approximately 35 <br /> inches. <br /> 14. During three of the four quarterly monitoring events conducted to date, the <br /> • concentrations of nitrate-nitrogen in all of the sample locations were consistent. In fact, <br /> the concentrations of nitrate-nitrogen upstream of the nursery's basin were frequently <br /> greater than the water within the basin (or its discharge, as applicable). The only <br /> exception was at the beginning of the irrigation season (Third Quarter 1998) prior to the <br /> nursery's reinstitution of treatment of their tailwater with KI-Nitrifier. <br /> 15. Kleinfelder recommends that the groundwater monitoring be continued. <br /> 16. Since surface water quality does not appear to be impacted significantly by Norman's <br /> Nursery's activities throughout the year (4 quarters) of monitoring that has taken place <br /> at the subject site, Kleinfelder recommends a decrease in the frequency of monitoring. <br /> Therefore, on behalf of Hakeem, Ellis & Simonelli and Norman's Nursery Kleinfelder <br /> recommends that the Monitoring & Reporting Program No. 97-811 be revised in the <br /> following manor: <br /> Norman's Nursery should continue to treat the tailwater within Basin B using KI- <br /> Nitrifier(or comparable treatment alternative) <br /> - daily surface water flow monitoring and observation should continue <br /> - weekly surface water sampling and analysis should be reduced in frequency to <br /> monthly <br /> - monthly surface water sampling and analysis should include all surface water <br /> sampling points detailed in M&RP No. 97-811 <br /> - additional surface water sampling for analysis should be conducted within 2 to 8 <br /> hours of the opening of the culverts and the release of any water to Potter <br /> Creek <br /> • <br /> 117226.E02/STO12R0696 Page 10 of 43 September 14, 2012 <br /> Copyright 2012 Kleinfelder <br />