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(NH 4 ) p
(NO 2 ) p
(N 2 O + N 2 ) g
(NO 3 ) p
K 5
K 3
K 9
K 4
K es
K 2
K 1
(NH 4 ) e
(NH 4 ) s
(NO 2 ) s
(NO 3 ) s
K se
KK 2
KK 7
KK 6
K 6
KK 8
(Org.N) i
FIGURE 5.2
A schematic representation of transformation of soil nitrogen. Terms K and KK refer to rate
coefficients and e, s, p, I, and g refer to exchangeable, solution, immobilized, and gaseous
phases, respectively. (From M. Mehran and K. K. Tanji. 1974. J. Environ. Qual. 3: 391-395. With
permission.)
and hydrologic processes controlling P transport must be clearly under-
stood. Many of the principles to be discussed for P reactions may in some
instances be applicable to other types of precipitation reactions (i.e., Al,
Fe, etc.). Mansell et al. (1977), investigating the transport of orthophos-
phate through saturated and unsaturated columns of a sandy soil, found
that a single process failed to describe P transport. Specifically, revers-
ible equilibrium adsorption-desorption relationship of the Freundlich
type inadequately described observed data. By coupling a first-order
kinetic expression with the classical transport equation and considering
nonlinear exchange of the Freundlich type, Mansell et al. (1977) substan-
tially improved the prediction of orthophosphate transport through soil
(Figure 5.3). They noted, however, that this model overpredicted the peak
1.0
No sink
0.8
- = 42.46 cm/h
0.6
Sink term
0.4
Q = α c C; α c = 0.2 h -1
Q = α s S; α s = 0.2 h -1
0.2
0 0
4
8
12
16
20
24
28
32
V/V o
FIGURE 5.3
Observed phosphate effluent condensations from the Al horizon of a sandy soil with predicted
curves determined using a one-site, nonlinear, nonequilibrium model with and without a sink
term for irreversible sorption and immobilization.
 
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