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ekienvironment <br /> & water <br /> The calculated gradient magnitude in the vicinity of LAA A23 was 0.0016 and the gradient azimuth <br /> was 260 degrees.The Spring 2023 gradient magnitude increased by 0.0013 and azimuth changed <br /> by -85 degrees relative to Fall 2022 (Table 4). Recycled water was last applied to LAA A23 on 24 <br /> September 2009. Therefore, changes in the calculated gradient beneath LAA A23 are due to <br /> factors other than irrigation with recycled water (for example, seasonal conditions and the <br /> corresponding changes in Mossdale area groundwater levels). <br /> Beneath the CLSP area, the water levels in the monitoring wells increased about 6.48 feet on <br /> average between Fall 2022 and Spring 2023 (Table 3). The inferred groundwater flow direction <br /> in Spring 2023 is generally away from the San Joaquin River toward the southeast, whereas <br /> groundwater flow in Fall 2022 was generally northeast from CLSP-3 towards CLSP-1. The <br /> calculated gradient in the vicinity of LAA A36 was 0.0007 and the gradient azimuth was 150 <br /> degrees. The Spring 2023 gradient magnitude increased by 0.0004 and the azimuth changed by <br /> 150 degrees relative to Fall 2022 (Table 4). <br /> Beneath River Islands, the water levels in monitoring wells increased by about 5.86 feet on <br /> average between Fall 2022 and Spring 2023 monitoring events (Table 3). The measured water <br /> levels and calculated gradients appear to be influenced by irrigation of River Islands agricultural <br /> fields, San Joaquin River, Old River, Paradise Cut,the drainage ditch located north and northeast <br /> of the LAAs, and construction dewatering activities in the area of LAA A30 (Figure 3). In the <br /> northwestern part of River Islands (beneath LAAs A30 and A31) inferred groundwater flow is <br /> generally away from the drainage ditch and towards well MWR-28, similar to Fall 2022. The <br /> measured water levels near LAA A30 appear to be influenced by continued construction <br /> dewatering activities in the vicinity of MWR-12, MWR-27, and MWR-28.10 MWR-12 was dry <br /> during the Spring 2023 semiannual monitoring event; therefore, no gradient was calculated <br /> within the vicinity of LAA A30 (Table 4). The calculated gradient beneath LAA A31 was 0.0014 <br /> indicating the gradient magnitude decreased by 0.0004; however, the azimuth was very similar <br /> to Fall 2022, as it only changed by 10 degrees (Table 4). In the southeastern part of River Islands <br /> (beneath LAA A28), the inferred groundwater flow direction is away from Paradise Cut and <br /> towards well MWR-3 (Figure 3), which is consistent with most past monitoring events. The <br /> calculated gradient beneath LAA A28 was 0.0032 and the azimuth was 45 degrees, indicating a <br /> 0.0026 increase in the gradient magnitude and -5 degree change in azimuth relative to Fall 2022 <br /> (Table 4). <br /> Beneath the CTF Facility, water levels in the monitoring wells increased about 6.17 feet on <br /> average between Fall 2022 and Spring 2023 (Table 3). Between these two sampling events, <br /> approximately 372 acre-feet of recycled water was applied to 1313-1. <br /> The Spring 2023 gradient directions are away from PB-1,which is the same as Fall 2022 (Table 4). <br /> Groundwater elevation contours (Figure 3) and gradient calculations indicate that inferred <br /> horizontal groundwater flow is generally to the west and southwest beneath Pond S5 and former <br /> LAS-2. The calculated gradient beneath PB-1 was 0.0034 and the azimuth was 315 degrees, <br /> indicating the Spring 2023 gradient magnitude increased by 0.003 and the azimuth changed by <br /> io Construction dewatering around MWR-12, MWR-27 and MWR-28 started during the Fall 2021 Monitoring Event. <br /> City of Lathrop 10 13 July 2023 <br /> EKI 1390088.03 <br />