AREA A/B ENGINEERING REPORT - Waste Management
AREA A/B ENGINEERING REPORT - Waste Management
AREA A/B ENGINEERING REPORT - Waste Management
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Geosyntec Consultants<br />
a practical standpoint, geomembrane manufacturers, like the producers of many consumer products,<br />
warranty geomembranes for far less than their service life. For example, a typical warranty for an<br />
exposed LLDPE geomembrane that is not protected from the environment by an overlying soil layer<br />
may be on the order of one year. This is intended to provide the warrantee sufficient time to install<br />
the liner and perceive manufacturing defects; it is not intended to correspond to service life.<br />
Therefore, the warranty period is clearly not relevant to the in-service performance of a<br />
geomembrane barrier used in a Subtitle D final cover system.<br />
The prescriptive low-permeability soil component of a cover system for a Subtitle-D landfill is a CCL<br />
which, when properly installed, provides an excellent barrier to infiltration. If maintained, the CCL<br />
should meet its hydraulic conductivity criterion for hundreds to thousands of years when used as a<br />
barrier in a MSW landfill. The high performance of final cover systems during the PCC period is<br />
evidenced by the low to negligible leachate generation rates observed for modern MSW landfills<br />
currently in PCC (see, for example, previous Figure B-1).<br />
The goals of final covers are changing to address new regulations and to optimize environmental<br />
stewardship. In December 2003, the Interstate Technical and Regulatory Council (ITRC), which<br />
represents a consensus of over 40 state regulatory agencies, Federal regulatory agencies, and<br />
many other stakeholders and is supported by the USPEA, published a “Technical and Regulatory<br />
Guidance for Design, Installation, and Monitoring of Alternative Final Landfill Covers”. The<br />
document evaluates the range of landfill covers and the features of each that provide benefits in<br />
terms of long-term stewardship and performance. The document concludes that alternative covers<br />
can provide protection equivalent to prescriptive Subtitle D covers with the added benefit of<br />
increased longevity and stability.<br />
B4.2.2 Maintenance of Final Cover Systems<br />
During the PCC period, the performance of the final cover system can be evaluated by monitoring<br />
leachate generation rates over time. If rates were to unexpectedly increase, the cause would be<br />
investigated. Although it has been speculated that final cover system failure is inevitable during the<br />
PCC period, such findings are not being observed at modern MSW landfills that are currently in PCC<br />
periods with properly maintained covers. The cover maintenance that is required for closed MSW<br />
landfills has primarily been related to cover system vegetation (e.g., mowing, tree removal, revegetating)<br />
and erosion and sediment control (e.g., removal of sediment from ditches and ponds,<br />
regrading the top deck to promote drainage). The effectiveness of the barrier layer in conventional<br />
cover systems is evidenced by measured overall reduction in leachate flow rates over time from the<br />
LCS (see Figures B-1 and B-2 and, secondarily, measurement of LFG emissions (Bonaparte, 1995;<br />
Othman, et al, 2002).<br />
An increasing number of landfills are being closed with an evapotranspirative (ET) final cover system<br />
(i.e., all-soil covers) rather than a prescriptive final cover system with a CCL/geomembrane barrier.<br />
The concern is that a CCL barrier will desiccate in arid and semi-arid climates if not protected by an<br />
overlying geomembrane and a sufficiently thick soil erosion layer. An ET final cover typically consists<br />
of more loosely compacted soils of sufficient thickness to optimally store and release water through ET<br />
processes. For this reason, ET covers tend to be thicker than conventional covers, and the soils are not<br />
MD10186.doc 131 29 March 2009