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AREA A/B ENGINEERING REPORT - Waste Management

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Geosyntec Consultants<br />

Leachate is liquid that drains through the disposed waste as the waste compresses in the landfill.<br />

When designing leachate management systems, the potential for leachate formation is assessed<br />

through the preparation of a water balance for the landfill. This involves summing inputs (the<br />

amount of water entering the landfill) and subtracting other outputs (the amount of water<br />

consumed in chemical reactions and the quantity leaving as water vapor). A water balance study<br />

at a landfill helps identify the significance of these various water components. This is important to<br />

leachate management in terms of determining needed storage, treatment, and disposal capacities<br />

and configuration. 7 Peak leachate flow rates generally decrease over time as active landfill<br />

areas are closed and improved infiltration control is achieved by the final cover system.<br />

An active gas management system (GMS) is designed and sized to collect generated LFG and to<br />

maintain appropriate negative pressures within the landfill to optimize gas collection efficiency<br />

and to reduce the potential of landfill gas migration or surface emissions. Design factors include<br />

current and future MSW intake, corresponding LFG generation and yield potential, field<br />

observations and testing, the size and characteristics of the permitted landfill area, surrounding<br />

terrain, and subsurface conditions. These factors will determine system performance and the<br />

means to control LFG migration and emissions.<br />

As with any civil engineering structure, consideration of the long-term geotechnical stability of the<br />

landfill is a key focus during the design process. Demonstrating both short- and long-term landfill<br />

stability are components of the design calculations and modeling performed during preparation<br />

of a permit application.<br />

2.2.3 Construction<br />

Following state agency approval of the landfill’s planning and design<br />

specifications, a permit is issued to begin construction, starting with the base liner,<br />

leachate collection and recovery system (LCRS), site access roads, and accessory<br />

operations facilities. Leachate is contained and recovered for proper disposal<br />

from the earliest phases of landfill use, thus supporting the effectiveness of the<br />

liner system. Liner systems are designed and constructed to contain leachate and gas within the<br />

landfill as well as to direct leachate and gas to their controls systems.<br />

Liner systems are typically constructed as a composite system of low permeability materials,<br />

including natural soils (compacted clay), geomembranes, and/or geosynthetic clay liners<br />

(materials used in construction of containment systems are discussed in more detail in Section 3.1).<br />

Both the liner system and LCRS are installed in accordance with a construction quality assurance<br />

(CQA) program. An independent program of third party CQA is required to inspect, test,<br />

document, and certify that the liner system is installed in accordance with design specifications<br />

and regulatory requirements.<br />

7 Estimates of leachate generation rates can be performed using several computer programs of which the USEPA’s<br />

Hydrogeologic Evaluation of Landfill Performance (HELP) model is the best known and most widely used. Seminal<br />

references on leachate generation include Peyton & Schroeder (1993) and Schroeder, et al (1994).<br />

MD10186.doc 29 29 March 2009

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