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Mr. Michael T. Goldstein <br /> October 18 , 1985 <br /> Page 2 <br /> program that can simulate solute transport in groundwater (Prickett, <br /> T. A. , and others; A Random Walk Solute Transport Model for Selected <br /> Groundwater Quality Evaluations, " Bulletin 65 of the Illinois State <br /> Water Survey) . The effects of dispersion and chemical reactions <br /> ( retardation) are included. <br /> The code can simulate nonsteady or steady flow problems in <br /> hetrogeneous aquifers under confined and/or unconfined and leaky <br /> conditions . The program covers pumping and injection by wells and <br /> allows specification of chemical constituent concentrations in any <br /> segment of the model. <br /> Further features of the program include variable grid size, printout <br /> of input data, sequential plots of solute concentration <br /> distributions , concentrations of water recharged to the modeled area , <br /> quantities of chemical constituents removed by pumpage and the <br /> effects of dispersion and dilution or mixing of waters having <br /> different solute concentrations. <br /> The basis for the solute transport calculation in this code is that <br /> the distribution of concentrations can be represented by the <br /> distribution of a finite number of discrete particles. Each particle <br /> is assigned a mass which represents the weight of pure solute <br /> dissolved in an element of aquifer to produce a convenient unit <br /> concentration, i .e. , 100 ppb for each particle in an element. <br /> The particles are removed by groundwater flow and the changes in <br /> concentration are controlled by dispersion, retardation, dilution, <br /> and mixing . The groundwater flow vector is entered as the regional <br /> velocity and modified as the head distribution is changed. The <br /> dispersion is calculated as a random process tending to a normal <br /> distribution moderated by longitutinal and transverse dispersivity. <br /> The retardation is a coefficient that includes adsorption, organic <br /> fixation, and biodegradation. <br /> Basic Transport Coefficient <br /> The basic transport coefficients defined for the shallow aquifer in <br /> the vicinity of the Georgia-Pacific plant are as follows : <br /> Tiansmissivity = 150 ,000 (gpd/ft ) <br /> Storage coefficient = 0 .01 (dimensionless) <br /> Hydraulic conductivity = 3 ,750 (gpd/sq ft) <br /> Porosity = 0 . 30 (dimensionless) <br /> Longitudinal dispersivity = 27 ( ft) <br /> Transverse dispersivity = 6.5 ( ft) <br /> Retardation coefficient = 1.0 (dimensionless) <br /> Regional X flow = -0 . 53 ( ft/day) <br /> Regional Y flow = 1 . 57 ( ft/day) <br /> Particle mass = 0 . 7488 ( lbs) <br /> BROWN AND CALDWLLL <br /> .. 6.0 N 1619'1 OUIp If I I% n Dd'Ip•Of I if Al JA NI bu,I If AVI 14tI I I I kp V1I I IH I <br />