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chapter 4: temperature inside the landfill

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K s<br />

= K e<br />

h = hmaxe<br />

( 1)<br />

* γ θ −<br />

−aθ<br />

* ( θ −θ<br />

ad )<br />

θ =<br />

( θ −θ<br />

s<br />

ad<br />

)<br />

(2-9)<br />

(2-10)<br />

(2-11)<br />

Where K is <strong>the</strong> hydraulic conductivity, Ks is <strong>the</strong> saturated hydraulic conductivity, h is <strong>the</strong><br />

suction head, hmax is <strong>the</strong> maximum suction head, a is <strong>the</strong> fitting parameter, γ is <strong>the</strong> fitting<br />

parameter, θ* is <strong>the</strong> normalized moisture content, θ is <strong>the</strong> moisture content, θs is <strong>the</strong> saturated<br />

moisture content, and θad is air, dry moisture content.<br />

Using exponential equations gave a highest value of hs at dry conditions (i.e. when θ<br />

equals zero) while at dry conditions, power equations give an infinite value.<br />

Uguccioni and Zeiss (1997) investigated <strong>the</strong> leachate movement through MSW using two<br />

models; a one-dimensional HELP model and two-domain model PREFLO. It was concluded that<br />

leachate flow in <strong>the</strong> <strong>landfill</strong> can be effectively modeled by a two-domain model which can<br />

simulate channel as well as matrix flow or by a one-domain approach which allows strongly<br />

varying flow parameters like hydraulic conductivity and effective storage.<br />

McCreanor and Reinhart (1999) modeled leachate recirculation in <strong>the</strong> <strong>landfill</strong>s using<br />

SUTRA which is based on <strong>the</strong> method of two-dimensional hybrid finite element and integrated<br />

finite difference. It was suggested in <strong>the</strong> study that heterogeneities in <strong>the</strong> waste lead to non-<br />

uniform wetting of <strong>the</strong> waste and homogenizing <strong>the</strong> waste mass would enhance uniform wetting.<br />

11

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