Agriculture Reference
In-Depth Information
transient water flow in a variably saturated rigid porous medium are (Simunek and
van Genuchten, 1995 ) as follows:
a v D g
∂θ
c 1
+ ∂ρ
s 1
+
a v g 1
D ij ,1
c 1
ij ,1
g 1
q i c 1
=
θ
+
Sc r ,1
t
t
t
x i
x j
x i
x j
x i
μ w ,1 + μ w ,1 )
μ s ,1 + μ s ,1 )
μ g 1 + μ g ,1 ) a v g 1 + γ w ,1 θ + γ s ,1 ρ + γ g ,1 a v
(7.7)
(
θ
c 1
(
ρ
s 1
(
a v D ij , k
∂θ
c k
+ ∂ρ
s k
+
a v g k
D ij ,1
c k
g k
q i c k
=
θ
+
Sc r , k
t
t
t
x i
x j
x i
x j
x i
μ w , k + μ w , k )
μ s , k + μ s , k )
μ g , k + μ g , k ) a v g k + μ w , k 1 θ
(
θ
c k
(
ρ
s k
(
c k 1 +
μ s , k 1 ρ
s k 1 + μ g , k 1 a v g k 1 + γ w , k θ + γ s , k ρ + γ g , k a v
k
ε
(2, n s )
(7.8)
where c, s, and g are solute concentrations in the liquid [ML -3 ], solid [MM -3 ],
and gaseous [ML -3 ] phases, respectively; q i is the i th component of the volumetric
flux density [LT -1 ];
μ g are first-order rate constants for solutes in the
liquid, solid, and gas phases [T -1 ], respectively;
μ w ,
μ s , and
μ g are similar first-
order rate constants providing connections between individual chain species;
μ w ,
μ s , and
γ w ,
γ g are zero-order rate constants for liquid [ML -3 T -1 ], solid [T -1 ], and gas
phases[ML -3 T -1 ], respectively;
γ s , and
is the soil bulk density [ML -3 ], a v is the air con-
tent [L -3 L -3 ], S is the sink term in the water flow, c r is the concentration of the sink
term [ML -3 ], D y w is the dispersion coefficient tensor [L 2 T -1 ] for the liquid phase,
and D y g is the diffusion coefficient tensor [L 2 T -1 ] for the gas phase. The subscript
w, s, and g correspond with the liquid, solid, and gas phases, respectively; while the
subscript k represents the k th chain number, and n s is the number of solutes involved
in the chain reaction.
ρ
7.4.4.2 One-Dimensional Transport
Solute transport equation for a homogeneous, isotropic porous medium during
steady-state unidirectional groundwater flow reduces to the following:
2 c
2 c
D T
D L
v
c
R
c
x 2 +
z λ
Rc
=
(7.9)
z 2
t
where
is a first-order degradation constant, D L and D T are the longitudinal and
transverse dispersion coefficients, respectively;
λ
ν
is the average pore water velocity
( q z /
) in the flow direction, R is the solute retardation factor, and z and x are the
spatial coordinates parallel and perpendicular to the direction of flow. The initial
solute-free medium is subjected to a solute source, c 0 , of unit concentration. The
θ
 
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