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User's guide of Proceessing Modflow 5.0

User's guide of Proceessing Modflow 5.0

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Processing <strong>Modflow</strong> 113<br />

MOC3D < Dispersion & Chemical Reaction...<br />

The types <strong>of</strong> reactions incorporated into MOC3D are restricted to those that can be represented<br />

by a first-order rate reaction, such as radioactive decay, or by a retardation factor, such as<br />

instantaneous, reversible, sorption-desorption reactions governed by a linear isotherm and<br />

constant distribution coefficient (K ).<br />

d<br />

Use the Dispersion / Chemical Reaction (MOC3D) dialog box (Fig. 3.36) to specify the<br />

required data for each model layer as described below.<br />

< Simulate Dispersion: Check this option, if dispersion should be included in the simulation.<br />

-1<br />

< First order decay rate 8 [T ] typically represents represents radioactive decay <strong>of</strong> both the<br />

free and sorbed solute. A radioactive decay rate is usually expressed as a half-life (t ). The<br />

1/2<br />

half-life is the time required for the concentration to decrease to one-half <strong>of</strong> the original<br />

value. 8 is calculted by:<br />

8 ' ln2<br />

t 1/2<br />

F ' &D @ dC<br />

dx<br />

D ( ' T @ D<br />

(3.32)<br />

2 -1<br />

< Effective molecular diffusion coefficient [L T ] describes the diffusive flux <strong>of</strong> a solute in<br />

water from an area <strong>of</strong> greater concentration toward an area where it is less concentrated. The<br />

mass flux is proportional to the concentration gradient and is given by Fick’s first law:<br />

(3.33)<br />

-2 -1 2 -1<br />

where F [ML T ] is the mass flux <strong>of</strong> solute per unit area per unit time; D [L T ] is the<br />

-3 -3 -1<br />

diffusion coefficient; C [ML ] is the solute concentration and dC/dx [ML L ] is the<br />

concentration gradient. In porous media, the solute mass cannot move as fast as the water,<br />

because the ions must flow through a longer pathways through the pore space and because<br />

<strong>of</strong> adsorption on the soil matrix. To account for this effects, an effective diffusion coefficient<br />

*<br />

D must be used.<br />

(3.34)<br />

According to Freeze and Cherry (1979), T ranges from 0.5 to 0.01 for laboratory studies <strong>of</strong><br />

diffusion <strong>of</strong> nonadsorbed ions in porous geologic materials. The diffusion coefficients D <strong>of</strong><br />

+ + 2+ 2+ - - 2-<br />

the major ions (Na , K , Mg , Ca , Cl , HCO 3 , SO 4 ) are temperature-dependent and range<br />

-9 -9 2<br />

from 1× 10 to 2× 10 m /s at 25 °C (Robinson and Stokes, 1965). At 5°C the coefficients<br />

are about 50% smaller. The molecular diffusion coefficient is generally very small and<br />

3.6.2 MOC3D

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