Environmental Engineering Reference
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where k 1 = k [ H 2 O 2 ] . The reaction is quite fast at high temperature and pH, and
it becomes quite difficult to be examined at 25 °C and pH 8. The reaction at 5 °C
and pH 3.5 followed first-order kinetics with respect to Fe(II) for seawater sam-
ples, giving k = 0.0385 ± 0.0009 min 1 and log k = 1.50 ± 0.02 ( k in M 1 s -1 )
(Millero and Sotolongo 1989 ). At higher pH and temperature, the second-order
reaction rate constants have been determined at the stoichiometric ratio [Fe(II)]/
[H 2 O 2 ] = 2, following Eq. ( 4.29 ) (Benson 1960 )
(4.29)
1 /[ Fe(II) ]= 1 /[ Fe(II) ] o + ( k / 2 ) t
where [Fe(II)] o is the initial concentration of Fe(II).
The rate constant k (M -1 s -1 ) for Eq. ( 4.29 ) is independent of pH below pH
4, and increases significantly at high pH values. It is a linear function of [H + ] or
[HO - ] from pH 6 to 8 in seawater. The effect of pH is not affected by a variation
of the temperature
The effects of temperature (T) and ionic strength ( I ) on k at pH 6 can be
expressed as (Eq. 4.30 ) (Millero and Sotolongo 1989 ):
log K = 13. 73 2, 948 / T 1. 70 I 1 / 2
(4.30)
+ 1. 20 I
The reaction rates can be depicted as (Eq. 4.31 ) (Millero and Sotolongo 1989 ):
d [ Fe(II) ]/ dt =− k 2 [ Fe(II) ][ H 2 O 2 ][ HO ]
(4.31)
where the values of k 2 are independent of temperature. This is attributed to the
fact that the activation energy is of the same order of magnitude as the heat of ion-
ization of water ( Δ H w * ). The effect of the ionic strength on log k 2 can be depicted
as (Eq. 4.32 ) (Millero and Sotolongo 1989 ):
log K 2 = 11. 72 2. 14 I 1 / 2
+ 1. 38 I
(4.32)
The overall reaction rate k over the entire range of pH, temperature and ionic
strength can be expressed by (Eq. 4.33 ) (Millero and Sotolongo 1989 ):
(4.33)
k = k o α Fe + k 1 α FeOH
where α Fe and α FeOH , k o and k 1 are the fractions of the two Fe(II) species and the
rate constants for the oxidation of Fe 2 + and FeOH + , respectively. The values of k o
and k 1 can be expressed by (Eqs. 4.34 , 4.35 ) (Millero and Sotolongo 1989 ):
(4.34)
log K 0 = 8. 37 1, 866 / T
log k 1 = 17. 26 2. 948 / T 1. 70 I 1 / 2 + 1. 20I
(4.35)
The addition of HCO 3 - at constant pH linearly increases the reaction rate, inde-
pendently of the temperature and salinity. This result can be attributed to FeCO 3 0
reacting faster than FeOH + with H 2 O 2 . At a given pH and ionic strength, the reac-
tion rates in seawater are almost the same as in NaCl. These results can explain
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