Geoscience Reference
In-Depth Information
m 3 , i.e., gramof phosphorus per
cubic meter); and k N ,1 / 2 and k P ,1 / 2 are the Michaelis-Menten half-saturation nitrogen
and phosphorus concentrations for phytoplankton growth, respectively. C NH 3 , C NO 3 ,
and C PO 4 are determined using Eqs. (12.78), (12.79), and (12.86), respectively.
Phytoplankton growth is a function of light intensity, until an optimal value is
reached. The light limitation factor can be determined by Smith's (1936), Steele's
(1962), or the half-saturation approach. The half-saturation approach gives
inorganic (dissolved) phosphorus concentration (gP
·
I z
k L ,1 / 2
f L
=
(12.67)
+
I z
where k L ,1 / 2 is the Michaelis-Menten half-saturation light intensity for phytoplankton
growth; and I z is the light intensity at a given height z and varies with z according to
Beer's law:
I z
=
I 0 exp
[− λ(
z s
z
) ]
(12.68)
where I 0 is the light intensity at the water surface, and
is the light extinction
coefficient. Note that the energy source for photosynthesis is the light in the range
of 400- to 700-nanometer wavelengths. It is called the photosynthetically active radi-
ation (PAR). PAR is different from the insolation J Tsw in Eq. (12.27), which is in the
entire spectrum of wavelengths (see Rounds et al ., 1999).
The light extinction coefficient
λ
is affected by phytoplankton, suspended sediments,
etc., in the water column. The following linear relation between
λ
λ
and C Phy is often
used:
λ = λ
+
k r a CChl C Phy
(12.69)
0
where
0 is the light extinction coefficient without phytoplankton, k r is a coefficient
for light attenuation by phytoplankton, and a CChl is the conversion factor of carbon
to chlorophyll of phytoplankton.
To consider the effects of both phytoplankton and suspended sediments on light
attenuation, Stefan et al . (1983) suggested the following relation:
λ
λ = λ
+
0.025 a CChl C Phy +
0.043 C s
(12.70)
0
m 1 , C Phy is in mgC
m 3 , and C s is the suspended sediment
λ
λ 0 are in l
·
·
where
and
m 3 .
The depth-averaged light limitation factor is obtained by integrating Eq. (12.67)
over the flow depth as
concentration in g
·
h ln k L ,1 / 2
+
I 0
1
λ
f L , av
=
(12.71)
I 0 e λ h
k L ,1 / 2
+
A byproduct of phytoplankton growth is dissolved oxygen. An additional source
of oxygen from phytoplankton growth occurs when the available ammonia nutrient
 
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