.MCAD 304020000 1 79 2207 0 .CMD PLOTFORMAT 0 0 1 1 1 0 0 1 1 0 0 1 1 1 0 0 1 1 0 1 0 0 1 1 NO-TRACE-STRING 0 2 1 0 1 1 NO-TRACE-STRING 0 3 2 0 1 1 NO-TRACE-STRING 0 4 3 0 1 1 NO-TRACE-STRING 0 1 4 0 1 1 NO-TRACE-STRING 0 2 5 0 1 1 NO-TRACE-STRING 0 3 6 0 1 1 NO-TRACE-STRING 0 4 0 0 1 1 NO-TRACE-STRING 0 1 1 0 1 1 NO-TRACE-STRING 0 2 2 0 1 1 NO-TRACE-STRING 0 3 3 0 1 1 NO-TRACE-STRING 0 4 4 0 1 1 NO-TRACE-STRING 0 1 5 0 1 1 NO-TRACE-STRING 0 2 6 0 1 1 NO-TRACE-STRING 0 3 0 0 1 1 NO-TRACE-STRING 0 4 1 0 1 1 NO-TRACE-STRING 0 1 1 21 15 0 0 3 .CMD FORMAT rd=d ct=10 im=i et=3 zt=15 pr=3 mass length time charge temperature tr=0 vm=0 .CMD SET ORIGIN 1 .CMD SET TOL 0.001000000000000 .CMD SET PRNCOLWIDTH 10 .CMD SET PRNPRECISION 4 .CMD PRINT_SETUP 1.000000 1.000000 1.200000 1.200000 0 .CMD HEADER_FOOTER 1 1 *empty* *empty* *empty* 0 1 *empty* B6^-^|P *empty* .CMD HEADER_FOOTER_FONT fontID=14 family=Arial points=10 bold=0 italic=0 underline=0 colrid=-1 .CMD HEADER_FOOTER_FONT fontID=15 family=Times^New^Roman points=12 bold=0 italic=0 underline=0 colrid=-1 .CMD DEFAULT_TEXT_PARPROPS 0 0 0 .CMD DEFINE_FONTSTYLE_NAME fontID=0 name=Variables .CMD DEFINE_FONTSTYLE_NAME fontID=1 name=Constants .CMD DEFINE_FONTSTYLE_NAME fontID=2 name=Text .CMD DEFINE_FONTSTYLE_NAME fontID=4 name=User^1 .CMD DEFINE_FONTSTYLE_NAME fontID=5 name=User^2 .CMD DEFINE_FONTSTYLE_NAME fontID=6 name=User^3 .CMD DEFINE_FONTSTYLE_NAME fontID=7 name=User^4 .CMD DEFINE_FONTSTYLE_NAME fontID=8 name=User^5 .CMD DEFINE_FONTSTYLE_NAME fontID=9 name=User^6 .CMD DEFINE_FONTSTYLE_NAME fontID=10 name=User^7 .CMD DEFINE_FONTSTYLE fontID=0 family=Times^New^Roman points=10 bold=0 italic=0 underline=0 colrid=-1 .CMD DEFINE_FONTSTYLE fontID=1 family=Times^New^Roman points=10 bold=0 italic=0 underline=0 colrid=-1 .CMD DEFINE_FONTSTYLE fontID=2 family=Times^New^Roman points=10 bold=1 italic=0 underline=0 colrid=1 .CMD DEFINE_FONTSTYLE fontID=4 family=Arial points=10 bold=0 italic=0 underline=0 colrid=-1 .CMD DEFINE_FONTSTYLE fontID=5 family=Courier^New points=10 bold=0 italic=0 underline=0 colrid=-1 .CMD DEFINE_FONTSTYLE fontID=6 family=System points=10 bold=0 italic=0 underline=0 colrid=-1 .CMD DEFINE_FONTSTYLE fontID=7 family=Script points=10 bold=0 italic=0 underline=0 colrid=-1 .CMD DEFINE_FONTSTYLE fontID=8 family=Roman points=10 bold=0 italic=0 underline=0 colrid=-1 .CMD DEFINE_FONTSTYLE fontID=9 family=Modern points=10 bold=0 italic=0 underline=0 colrid=-1 .CMD DEFINE_FONTSTYLE fontID=10 family=Times^New^Roman points=10 bold=0 italic=0 underline=0 colrid=-1 .CMD UNITS U=1 .CMD DIMENSIONS_ANALYSIS 0 0 .CMD FILENAME fit fife-fi.prn .CMD FILENAME fet fife-fe.prn .CMD COLORTAB_ENTRY 0 0 0 .CMD COLORTAB_ENTRY 128 0 0 .CMD COLORTAB_ENTRY 0 128 0 .CMD COLORTAB_ENTRY 128 128 0 .CMD COLORTAB_ENTRY 0 0 128 .CMD COLORTAB_ENTRY 128 0 128 .CMD COLORTAB_ENTRY 0 128 128 .CMD COLORTAB_ENTRY 128 128 128 .CMD COLORTAB_ENTRY 192 192 192 .CMD COLORTAB_ENTRY 255 0 0 .CMD COLORTAB_ENTRY 0 255 0 .CMD COLORTAB_ENTRY 255 255 0 .CMD COLORTAB_ENTRY 0 0 255 .CMD COLORTAB_ENTRY 255 0 255 .CMD COLORTAB_ENTRY 0 255 255 .CMD COLORTAB_ENTRY 255 255 255 .CMD COLORTAB_ENTRY 64 0 64 .TXT 3 1 1798 0 0 Cg a63.000000,63.000000,45 {\rtf\ansi \deff0{\colortbl;\red0\green0\blue0;\red64\green0\blue64;}{ \fonttbl{\f0\fcharset0\fnil Times New Roman;}}\plain\cf1\fs20\b \pard { \cf2\fs28 B6. Infiltration/Exfiltration Model (}{\cf2\fs28 INFEXF)}} .TXT 5 1 872 0 0 Cg a70.000000,70.000000,15 {\rtf\ansi \deff0{\colortbl;\red0\green0\blue0;\red64\green0\blue64;}{ \fonttbl{\f0\fcharset0\fnil Times New Roman;}}\plain\cf1\fs20\b \pard { \cf2 A. Description}} .TXT 4 0 871 0 0 Cg a69.000000,69.000000,1360 {\rtf\ansi \deff0{\colortbl;\red0\green0\blue0;\red64\green0\blue64;}{ \fonttbl{\f0\fcharset0\fnil Times New Roman;}}\plain\cf1\fs20\b \pard { \cf2 The vertical movement of soil water between the surface and the water table can be divided into two processes according to the predominant forces involved: (1) infiltration and (2) exfiltration (evaportranspiration). An infiltration/exfiltration model (INFEXF) developed by Eagleson (1978) was selected to estimate the water infiltration during wetting season and exfiltration during drying season. Infiltration and exfiltration are described by Philip's equation, which assumes the medium to be effectively semi-infinite and the internal soil water content at the beginning of each storm and interstorm period is assumed to be uniform at its long term space-time average. The exfiltration equation is modified for presence of natural vegetation through the approximate introduction of a distributed sink representing the moisture extraction by plant roots. Two cases were presented in this application. The first case is the water infiltration into a sandy loam during storms. A boundary condition with saturated water content on the soil surface is assumed. In this case, rainfall intensity is assumed to be greater than the infiltration capacity. The second case is the exfiltration during drying surface (interstorm) periods with a dry soil surface and under the assumption that potential evaporation is greater than the exfiltration capacity.}} .TXT 28 0 1991 0 0 Cg a70.000000,70.000000,26 {\rtf\ansi \deff0{\colortbl;\red0\green0\blue0;\red64\green0\blue64;}{ \fonttbl{\f0\fcharset0\fnil Times New Roman;}}\plain\cf1\fs20\b \pard { \cf2 B. Definition of Variables}} .EQN 5 2 2008 0 0 {0:\q.s}NAME:0.41 .TXT 0 26 1816 0 0 Cg a58.000000,58.000000,64 {\rtf\ansi \deff0{\colortbl;\red0\green0\blue0;\red64\green0\blue64;}{ \fonttbl{\f0\fcharset0\fnil Times New Roman;}}\plain\cf1\fs20\b \pard { \cf2 Saturated volumetric water content at the soil surface (cm}{\cf2 \up 3}{\cf2 /cm}{\cf2\up 3}{\cf2 )}} .EQN 3 -26 2009 0 0 {0:\q.0}NAME:0.07 .TXT 0 26 1818 0 0 Cg a58.000000,58.000000,43 {\rtf\ansi \deff0{\colortbl;\red0\green0\blue0;\red64\green0\blue64;}{ \fonttbl{\f0\fcharset0\fnil Times New Roman;}}\plain\cf1\fs20\b \pard { \cf2 Initial volumetric water content (cm}{\cf2\up 3}{\cf2 /cm}{\cf2 \up 3}{\cf2 )}{\cf2 }} .EQN 4 -26 2010 0 0 {0:K.s}NAME:2.59 .TXT 0 26 1820 0 0 Cg a58.000000,58.000000,39 {\rtf\ansi \deff0{\colortbl;\red0\green0\blue0;\red64\green0\blue64;}{ \fonttbl{\f0\fcharset0\fnil Times New Roman;}}\plain\cf1\fs20\b \pard { \cf2 Saturated hydrualic conductivity (cm/h)}} .EQN 4 -26 2014 0 0 {0:\l}NAME:0.89 .TXT 0 26 1822 0 0 Cg a58.000000,58.000000,28 {\rtf\ansi \deff0{\colortbl;\red0\green0\blue0;\red64\green0\blue64;}{ \fonttbl{\f0\fcharset0\fnil Times New Roman;}}\plain\cf1\fs20\b \pard { \cf2 Pore size distribution index}} .EQN 5 -26 2015 0 0 {0:c}NAME:(2+3*{0:\l}NAME)/({0:\l}NAME) .TXT 0 26 1993 0 0 Cg a49.000000,49.000000,47 {\rtf\ansi \deff0{\colortbl;\red0\green0\blue0;}{\fonttbl{\f0\fcharset0 \fnil Times New Roman;}}\plain\cf1\fs20\b \pard Soil index based on the pore distribution index} .TXT 7 -29 1980 0 0 Cg a71.000000,71.000000,24 {\rtf\ansi \deff0{\colortbl;\red0\green0\blue0;}{\fonttbl{\f0\fcharset0 \fnil Times New Roman;}}\plain\cf1\fs20\b \pard C. Equations and Results} .TXT 5 5 1981 0 0 Cg a70.000000,70.000000,37 {\rtf\ansi \deff0{\colortbl;\red0\green0\blue0;\red64\green0\blue64;}{ \fonttbl{\f0\fcharset0\fnil Times New Roman;}}\plain\cf1\fs20\b \pard { \cf2 a. Infiltration during Rainy Seasons}} .EQN 7 -2 1959 0 0 {0:t}NAME:1;24 .TXT 0 44 2107 0 0 Cg a58.000000,58.000000,8 {\rtf\ansi \deff0{\colortbl;\red0\green0\blue0;\red64\green0\blue64;}{ \fonttbl{\f0\fcharset0\fnil Times New Roman;}}\plain\cf1\fs20\b \pard { \cf2 Time (h)}} .EQN 3 -44 2002 0 0 {0:\q.1}NAME:0.41 .TXT 0 44 2108 0 0 Cg a58.000000,58.000000,40 {\rtf\ansi \deff0{\colortbl;\red0\green0\blue0;\red64\green0\blue64;}{ \fonttbl{\f0\fcharset0\fnil Times New Roman;}}\plain\cf1\fs20\b \pard { \cf2 Soil water content at surface (cm}{\cf2\up 3}{\cf2 /cm}{\cf2\up 3}{ \cf2 )}} .EQN 5 -44 1684 0 0 {0:S}NAME({0:\q}NAME):({0:\q}NAME)/({0:\q.s}NAME) .TXT 0 44 1948 0 0 Cg a58.000000,58.000000,22 {\rtf\ansi \deff0{\colortbl;\red0\green0\blue0;\red64\green0\blue64;}{ \fonttbl{\f0\fcharset0\fnil Times New Roman;}}\plain\cf1\fs20\b \pard { \cf2 Degree of saturation}{\cf2 }} .EQN 6 -44 2033 0 0 {0:K}NAME({0:\q}NAME):{0:K.s}NAME*(({0:S}NAME({0:\q}NAME)))^({0:c}NAME) .TXT 0 44 2037 0 0 Cg a31.000000,31.000000,29 {\rtf\ansi \deff0{\colortbl;\red0\green0\blue0;}{\fonttbl{\f0\fcharset0 \fnil Times New Roman;}}\plain\cf1\fs20\b \pard Hydraulic conductivity (cm/h)} .EQN 6 -44 1964 0 0 {0:\Y1}NAME:-13.33 .TXT 0 44 1952 0 0 Cg a57.000000,57.000000,39 {\rtf\ansi \deff0{\colortbl;\red0\green0\blue0;\red64\green0\blue64;}{ \fonttbl{\f0\fcharset0\fnil Times New Roman;}}\plain\cf1\fs20\b \pard { \cf2 Near saturated soil water suction (cm) }} .TXT 7 0 1953 0 0 Cg a46.000000,46.000000,23 {\rtf\ansi \deff0{\colortbl;\red0\green0\blue0;\red64\green0\blue64;}{ \fonttbl{\f0\fcharset0\fnil Times New Roman;}}\plain\cf1\fs20\b \pard { \cf2 Soil water suction (cm)}} .TXT 0 29 2194 0 0 Cg a79.000000,79.000000,3 {\rtf\ansi \deff0{\colortbl;\red0\green0\blue0;}{\fonttbl{\f0\fcharset0 \fnil Times New Roman;}}\plain\cf1\fs20\b \pard (1)} .EQN 1 -73 2189 0 0 {0:\Y}NAME({0:\q}NAME):{0:\Y1}NAME*({0:S}NAME({0:\q}NAME))^((-1)/({0:\l}NAME)) .EQN 4 0 2191 0 0 {0:D}NAME({0:\q}NAME):{0:K}NAME({0:\q}NAME)*{0:\q}NAME"({0:\Y}NAME({0:\q}NAME)) .TXT 0 44 2174 0 0 Cg a46.000000,46.000000,30 {\rtf\ansi \deff0{\colortbl;\red0\green0\blue0;\red64\green0\blue64;}{ \fonttbl{\f0\fcharset0\fnil Times New Roman;}}\plain\cf1\fs20\b \pard { \cf2 Soil water diffusivity (cm}{\cf2\up 2}{\cf2 /h)}} .TXT 0 29 2196 0 0 Cg a79.000000,79.000000,3 {\rtf\ansi \deff0{\colortbl;\red0\green0\blue0;}{\fonttbl{\f0\fcharset0 \fnil Times New Roman;}}\plain\cf1\fs20\b \pard (2)} .EQN 9 -73 2175 0 0 {0:Di}NAME:(5)/(3)*(({0:\q.1}NAME-{0:\q.0}NAME))^(-((5)/(3)))*({0:\q.0}NAME&{0:\q.1}NAME`(({0:\q}NAME-{0:\q.0}NAME))^((2)/(3))*{0:D}NAME({0:\q}NAME)&{0:\q}NAME) .TXT 0 44 2176 0 0 Cg a35.000000,35.000000,39 {\rtf\ansi \deff0{\colortbl;\red0\green0\blue0;\red64\green0\blue64;}{ \fonttbl{\f0\fcharset0\fnil Times New Roman;}{\f1\fcharset2\fnil Symbol;}} \plain\cf1\fs20\b \pard {\cf2 Diffusivity over range }{\cf2\f1 q}{\cf2 \f1\dn 1}{\cf2 -}{\cf2\f1 q}{\dn 0}{\cf2 , (cm/h}{\cf2\up 1/2}{\cf2 )}} .TXT 0 29 2198 0 0 Cg a79.000000,79.000000,3 {\rtf\ansi \deff0{\colortbl;\red0\green0\blue0;}{\fonttbl{\f0\fcharset0 \fnil Times New Roman;}}\plain\cf1\fs20\b \pard (3)} .EQN 4 -44 2177 0 0 {0:Di}NAME={0}?_n_u_l_l_ .EQN 6 -29 2178 0 0 {0:S.i}NAME:2*({0:\q.1}NAME-{0:\q.0}NAME)*((({0:Di}NAME)/({0:\p}NAME)))^((1)/(2)) .TXT 0 44 2179 0 0 Cg a45.000000,45.000000,20 {\rtf\ansi \deff0{\colortbl;\red0\green0\blue0;\red64\green0\blue64;}{ \fonttbl{\f0\fcharset0\fnil Times New Roman;}}\plain\cf1\fs20\b \pard { \cf2 Sorptivity (cm/h}{\cf2\up 1/2}{\cf2 )}} .TXT 1 29 2199 0 0 Cg a79.000000,79.000000,3 {\rtf\ansi \deff0{\colortbl;\red0\green0\blue0;}{\fonttbl{\f0\fcharset0 \fnil Times New Roman;}}\plain\cf1\fs20\b \pard (4)} .EQN 7 -73 2180 0 0 ({0:fi}NAME)[({0:t}NAME):(1)/(2)*{0:S.i}NAME*({0:t}NAME)^((-1)/(2))+(1)/(2)*({0:K}NAME({0:\q.1}NAME)+{0:K}NAME({0:\q.0}NAME)) .TXT 0 44 2181 0 0 Cg a43.000000,43.000000,24 {\rtf\ansi \deff0{\colortbl;\red0\green0\blue0;\red64\green0\blue64;}{ \fonttbl{\f0\fcharset0\fnil Times New Roman;}}\plain\cf1\fs20\b \pard { \cf2 Infiltration rate (cm/h)}} .TXT 0 29 2200 0 0 Cg a79.000000,79.000000,3 {\rtf\ansi \deff0{\colortbl;\red0\green0\blue0;}{\fonttbl{\f0\fcharset0 \fnil Times New Roman;}}\plain\cf1\fs20\b \pard (5)} .EQN 5 -58 2182 0 0 {0:K}NAME({0:\q.1}NAME)={0}?_n_u_l_l_ .EQN 0 12 2183 0 0 {0:K}NAME({0:\q.0}NAME)={0}?_n_u_l_l_ .EQN 5 -25 2184 0 0 {0:t}NAME= .EQN 0 9 2185 0 0 ({0:fi}NAME)[({0:t}NAME)= .EQN 7 17 1721 0 0 &&(_n_u_l_l_&_n_u_l_l_)&({0:fi}NAME)[({0:t}NAME)@&&(_n_u_l_l_&_n_u_l_l_)&{0:t}NAME 0 0 1 1 1 0 0 1 1 Time (h) 0 0 1 1 1 0 0 1 1 Infiltration Rate (cm/h) 0 1 0 0 1 1 NO-TRACE-STRING 0 2 1 0 1 1 NO-TRACE-STRING 0 3 2 0 1 1 NO-TRACE-STRING 0 4 3 0 1 1 NO-TRACE-STRING 0 1 4 0 1 1 NO-TRACE-STRING 0 2 5 0 1 1 NO-TRACE-STRING 0 3 6 0 1 1 NO-TRACE-STRING 0 4 0 0 1 1 NO-TRACE-STRING 0 1 1 0 1 1 NO-TRACE-STRING 0 2 2 0 1 1 NO-TRACE-STRING 0 3 3 0 1 1 NO-TRACE-STRING 0 4 4 0 1 1 NO-TRACE-STRING 0 1 5 0 1 1 NO-TRACE-STRING 0 2 6 0 1 1 NO-TRACE-STRING 0 3 0 0 1 1 NO-TRACE-STRING 0 4 1 0 1 1 NO-TRACE-STRING 0 1 1 21 15 10 0 2 .TXT 26 3 1799 0 0 Cg a29.875000,29.875000,75 {\rtf\ansi \deff0{\colortbl;\red0\green0\blue0;\red64\green0\blue64;}{ \fonttbl{\f0\fcharset0\fnil Times New Roman;}}\plain\cf1\fs20\b \pard { \cf2 Figure B6-1. Water infiltration as a function of time during rainy season.}} .TXT 26 -28 2186 0 0 Cg a66.000000,66.000000,37 {\rtf\ansi \deff0{\colortbl;\red0\green0\blue0;\red64\green0\blue64;}{ \fonttbl{\f0\fcharset0\fnil Times New Roman;}}\plain\cf1\fs20\b \pard { \cf2 b. Exfiltration During Drying Season}} .EQN 6 -4 2139 0 0 {0:t}NAME:1;24 .TXT 0 43 2140 0 0 Cg a42.000000,42.000000,8 {\rtf\ansi \deff0{\colortbl;\red0\green0\blue0;\red64\green0\blue64;}{ \fonttbl{\f0\fcharset0\fnil Times New Roman;}}\plain\cf1\fs20\b \pard { \cf2 Time (h)}} .EQN 4 -43 2141 0 0 {0:\q.1}NAME:0.0001 .TXT 0 43 2142 0 0 Cg a58.000000,58.000000,44 {\rtf\ansi \deff0{\colortbl;\red0\green0\blue0;\red64\green0\blue64;}{ \fonttbl{\f0\fcharset0\fnil Times New Roman;}}\plain\cf1\fs20\b \pard { \cf2 Soil water content at dry surface (cm}{\cf2\up 3}{\cf2 /cm}{\cf2 \up 3}{\cf2 )}} .EQN 4 -43 2143 0 0 {0:\q.0}NAME:0.15 .TXT 0 43 2144 0 0 Cg a58.000000,58.000000,37 {\rtf\ansi \deff0{\colortbl;\red0\green0\blue0;\red64\green0\blue64;}{ \fonttbl{\f0\fcharset0\fnil Times New Roman;}}\plain\cf1\fs20\b \pard { \cf2 Initial soil water content (cm}{\cf2\up 3}{\cf2 /cm}{\cf2\up 3}{ \cf2 )}} .EQN 4 -43 2145 0 0 {0:\Y1}NAME:-13.33 .TXT 0 43 2146 0 0 Cg a57.000000,57.000000,39 {\rtf\ansi \deff0{\colortbl;\red0\green0\blue0;\red64\green0\blue64;}{ \fonttbl{\f0\fcharset0\fnil Times New Roman;}}\plain\cf1\fs20\b \pard { \cf2 Near saturated soil water suction (cm)}{\cf2 }} .EQN 5 -43 2147 0 0 {0:Ev}NAME:0.05 .TXT 0 43 2148 0 0 Cg a58.000000,58.000000,25 {\rtf\ansi \deff0{\colortbl;\red0\green0\blue0;\red64\green0\blue64;}{ \fonttbl{\f0\fcharset0\fnil Times New Roman;}}\plain\cf1\fs20\b \pard { \cf2 Transpiration rate (cm/h)}} .EQN 4 -43 2149 0 0 {0:M}NAME:0.2 .TXT 0 43 2150 0 0 Cg a56.000000,56.000000,34 {\rtf\ansi \deff0{\colortbl;\red0\green0\blue0;\red64\green0\blue64;}{ \fonttbl{\f0\fcharset0\fnil Times New Roman;}}\plain\cf1\fs20\b \pard { \cf2 Vegetated fraction of land surface}} .EQN 5 -43 2151 0 0 {0:\Y}NAME({0:\q}NAME):{0:\Y1}NAME*({0:S}NAME({0:\q}NAME))^((-{0}1)/({0:\l}NAME)) .TXT 0 43 2152 0 0 Cg a46.000000,46.000000,23 {\rtf\ansi \deff0{\colortbl;\red0\green0\blue0;\red64\green0\blue64;}{ \fonttbl{\f0\fcharset0\fnil Times New Roman;}}\plain\cf1\fs20\b \pard { \cf2 Soil water suction (cm)}} .TXT 0 31 2202 0 0 Cg a79.000000,79.000000,3 {\rtf\ansi \deff0{\colortbl;\red0\green0\blue0;}{\fonttbl{\f0\fcharset0 \fnil Times New Roman;}}\plain\cf1\fs20\b \pard (6)} .EQN 5 -74 2153 0 0 {0:D}NAME({0:\q}NAME):{0:K}NAME({0:\q}NAME)*{0:\q}NAME"({0:\Y}NAME({0:\q}NAME)) .TXT 0 43 2154 0 0 Cg a46.000000,46.000000,30 {\rtf\ansi \deff0{\colortbl;\red0\green0\blue0;\red64\green0\blue64;}{ \fonttbl{\f0\fcharset0\fnil Times New Roman;}}\plain\cf1\fs20\b \pard { \cf2 Soil water diffusivity (cm}{\cf2\up 2}{\cf2 /h)}} .TXT 0 31 2203 0 0 Cg a79.000000,79.000000,3 {\rtf\ansi \deff0{\colortbl;\red0\green0\blue0;}{\fonttbl{\f0\fcharset0 \fnil Times New Roman;}}\plain\cf1\fs20\b \pard (7)} .EQN 9 -74 2155 0 0 {0:De}NAME:(1.85)*(({0:\q.0}NAME-{0:\q.1}NAME))^(-(1.85))*({0:\q.1}NAME&{0:\q.0}NAME`(({0:\q.0}NAME-{0:\q}NAME))^(0.85)*{0:D}NAME({0:\q}NAME)&{0:\q}NAME) .TXT 0 43 2156 0 0 Cg a25.000000,25.000000,30 {\rtf\ansi \deff0{\colortbl;\red0\green0\blue0;\red64\green0\blue64;}{ \fonttbl{\f0\fcharset0\fnil Times New Roman;}}\plain\cf1\fs20\b \pard { \cf2 Desorption diffusivity (cm}{\cf2\up 2}{\cf2 /h)}} .TXT 0 31 2204 0 0 Cg a79.000000,79.000000,3 {\rtf\ansi \deff0{\colortbl;\red0\green0\blue0;}{\fonttbl{\f0\fcharset0 \fnil Times New Roman;}}\plain\cf1\fs20\b \pard (8)} .EQN 6 -48 2157 0 0 {0:De}NAME={0}?_n_u_l_l_ .EQN 4 -26 2158 0 0 {0:Se}NAME:2*({0:\q.0}NAME-{0:\q.1}NAME)*((({0:De}NAME)/({0:\p}NAME)))^((1)/(2)) .TXT 1 43 2159 0 0 Cg a45.000000,45.000000,33 {\rtf\ansi \deff0{\colortbl;\red0\green0\blue0;\red64\green0\blue64;}{ \fonttbl{\f0\fcharset0\fnil Times New Roman;}}\plain\cf1\fs20\b \pard { \cf2 Exfiltration sorptivity (cm/h}{\cf2\up 1/2}{\cf2 )}} .TXT 0 31 2205 0 0 Cg a79.000000,79.000000,3 {\rtf\ansi \deff0{\colortbl;\red0\green0\blue0;}{\fonttbl{\f0\fcharset0 \fnil Times New Roman;}}\plain\cf1\fs20\b \pard (9)} .EQN 3 -51 2160 0 0 {0:Se}NAME={0}?_n_u_l_l_ .EQN 6 -23 2161 0 0 ({0:fe}NAME)[({0:t}NAME):(1)/(2)*{0:Se}NAME*({0:t}NAME)^((-1)/(2))-(1)/(2)*({0:K}NAME({0:\q.1}NAME)+{0:K}NAME({0:\q.0}NAME))-{0:M}NAME*{0:Ev}NAME .TXT 1 43 2162 0 0 Cg a43.000000,43.000000,24 {\rtf\ansi \deff0{\colortbl;\red0\green0\blue0;\red64\green0\blue64;}{ \fonttbl{\f0\fcharset0\fnil Times New Roman;}}\plain\cf1\fs20\b \pard { \cf2 Exfiltration rate (cm/h)}} .TXT 0 30 2207 0 0 Cg a79.000000,79.000000,4 {\rtf\ansi \deff0{\colortbl;\red0\green0\blue0;}{\fonttbl{\f0\fcharset0 \fnil Times New Roman;}}\plain\cf1\fs20\b \pard (10)} .EQN 9 -72 2187 0 0 {0:t}NAME= .EQN 0 7 2188 0 0 ({0:fe}NAME)[({0:t}NAME)= .EQN 28 23 2110 0 0 &&(_n_u_l_l_&_n_u_l_l_)&({0:fe}NAME)[({0:t}NAME)@&&(_n_u_l_l_&_n_u_l_l_)&{0:t}NAME 0 0 1 1 1 0 0 1 1 Time (h) 0 0 1 1 1 0 0 1 1 Exfiltration rate (cm/h) 0 1 0 0 1 1 NO-TRACE-STRING 0 2 1 0 1 1 NO-TRACE-STRING 0 3 2 0 1 1 NO-TRACE-STRING 0 4 3 0 1 1 NO-TRACE-STRING 0 1 4 0 1 1 NO-TRACE-STRING 0 2 5 0 1 1 NO-TRACE-STRING 0 3 6 0 1 1 NO-TRACE-STRING 0 4 0 0 1 1 NO-TRACE-STRING 0 1 1 0 1 1 NO-TRACE-STRING 0 2 2 0 1 1 NO-TRACE-STRING 0 3 3 0 1 1 NO-TRACE-STRING 0 4 4 0 1 1 NO-TRACE-STRING 0 1 5 0 1 1 NO-TRACE-STRING 0 2 6 0 1 1 NO-TRACE-STRING 0 3 0 0 1 1 NO-TRACE-STRING 0 4 1 0 1 1 NO-TRACE-STRING 0 1 1 21 15 10 0 2 .TXT 30 4 2109 0 0 Cg a30.750000,30.750000,76 {\rtf\ansi \deff0{\colortbl;\red0\green0\blue0;\red64\green0\blue64;}{ \fonttbl{\f0\fcharset0\fnil Times New Roman;}}\plain\cf1\fs20\b \pard { \cf2 Figure B6-2. Water exfiltration as a function of time during drying season.}} .TXT 17 -37 1978 0 0 Cg a72.000000,72.000000,13 {\rtf\ansi \deff0{\colortbl;\red0\green0\blue0;\red64\green0\blue64;}{ \fonttbl{\f0\fcharset0\fnil Times New Roman;}}\plain\cf1\fs20\b \pard { \cf2 D. Discussion}} .TXT 5 2 1944 0 0 Cg a66.000000,66.000000,571 {\rtf\ansi \deff0{\colortbl;\red0\green0\blue0;\red64\green0\blue64;}{ \fonttbl{\f0\fcharset0\fnil Times New Roman;}}\plain\cf1\fs20\b \pard { \cf2 Water Infiltration into and exfiltration out of soil surface as a function of time is shown in Figures B6-1 and B6-2, respectively. }{ \cf2 Figure B6-1 shows a typical soil infiltration pattern, with an infiltration rate relatively high at the onset of the infiltration, then decreasing, and eventually approaching a constant rate. Figure B6-2 (Case 2) illustrates that exfiltration (actual evaporation) decreases with time. Nagative value of exfiltration indicates that exfiltration has ceased (}{\cf2 at the time of 11 hours}{\cf2 in this case) but transpiration is still going on.}}