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y <br /> r <br /> Taj M. Bahadori -2- 25 January 2019 <br /> Foothill Landfill <br /> Stockton <br /> 1. The approved components of the liner/final cover system will not be eliminated; <br /> 2. The engineering properties of the liner/final cover system components will not be <br /> substantially reduced; and <br /> 3. The proposed changes to the liner/cover system must be at least as protective of water <br /> quality as the design prescribed under the WDRs. <br /> The Liner EAD Report proposes replacing the LCRS gravel blanket layer over the base liner <br /> with a geocomposite drainage layer due to the high cost and lack of availability of suitable <br /> local gravel. No modification of the LCRS sump and sideslope EAD designs under the WDRs <br /> is being proposed. As such, the proposed design modification does not involve elimination of <br /> any liner components per Item 1 above. <br /> The relevant engineering properties of the blanket LCRS layer (Item 2 above) include the <br /> following: <br /> • Hydraulic Head — must be less than 30 cm (11.8 inches) per Subtitle D (40 CFR 258.4(a)(2)) <br /> • Flow Capacity— LCRS must be able to handle at least twice the anticipated maximum daily <br /> leachate flows per Title 27, section 2O43O(b); and <br /> • Material Strength - must be able to withstand compressive loads of overlying wastes, cover and <br /> landfill equipment per Title 27, section 2043O(e). <br /> The proposed modified EAD design was evaluated for the above properties using field data from <br /> adjacent Module 2A for comparison. Hydraulic modeling of the proposed design under estimated <br /> critical conditions indicated a maximum head on the base liner of 0.06 inches, much less than the <br /> typical geocomposite thickness of 0.3 inches.' The peak leachate drainage rate for the LCRS <br /> geocomposite was calculated to be 0.34 inches/day (9,240 gal/ac/day), about 2.6 times higher than <br /> the actual peak leachate drainage rate of 0.13 inches/day (3,460 gal/ac/day) at Module 2A based <br /> on 2017 leachate monitoring data. These results support a conclusion that the proposed LCRS <br /> design modification meets Title 27 and Subtitle D minimum standards for design head and flow <br /> capacity. <br /> After correction for various safety factors (clogging, material creep, and design), a design <br /> transmissivity for the geocomposite was then calculated as a function of the peak drainage rate <br /> from the HELP analyses, maximum distance to LCRS pipe, pipe hydraulic conductivity, and slope <br /> of the drainage layer. Design transmissivities for module construction quality assurance (CQA) <br /> testing were then calculated for various landfill development stages, including early development <br /> (15 vertical feet), interim development (145 feet of waste), and the maximum future build-out for <br /> LF-2 anticipated by the Discharger(300 feet). The results indicated corresponding minimum <br /> required 100-hour design transmissivities of 7.1x10-4 m2/s, 2.9 x10-4 m2/s, and 3.5x10-4 m2/s, <br /> respectively. Corresponding minimum required compressive strengths (including a safety factor of <br /> 1.5) were 1,500 psf, 16,500 psf and 38,250 psf. The report indicates that geocomposite LCRS <br /> products are available with minimum transmissivities and compressive strengths capable of <br /> withstanding these corresponding loads, including safety factor. <br /> 1 Hydraulic modelling for leachate head and flow rate was conducted using the Hydraulic Evaluation of Landfill <br /> Performance(HELP) program under assumed critical conditions(e.g.,15-foot waste column,wettest 10-year period <br /> on record). Only the LCRS blanket layer was included in this analysis, not the LCRS piping. <br />