Chemistry Reference
In-Depth Information
1.0
HOSCN
H
OBr
HOCl
0.8
0.6
0.4
0.2
OBr
-
OCl
-
-
OSCN
0.0
4.0
5.0
6.0
7.0
8.0
9.0
10.0
pH
Figure 3.2.
The species of aqueous Cl
2
, Br
2
, and HOSCN as a function of pH at 25°C.
of the compound, which contribute to an overall second-order reaction. The
second-order rate constants (
k
) of HOCl and OCl
−
for a particular compound
varied significantly with pH in the chlorination reactions [19]. HOCl was gener-
ally the major reactive species. The variation of HOCl species as a function of
pH is presented in Figure 3.2. The reactivity of Cl
2
with inorganic molecules
generally derived from an initial electrophilic attack on HOCl and
k
for organic
compounds varied from <10
−1
to 10
9
/M/s. The possible pathways in the reaction
mechanism include oxidation, addition, and electrophilic substitutions [19]. In
a recent study, the roles of chlorine monoxide (Cl
2
O) and Cl
2
have been dem-
onstrated in the chlorination of molecules that are of environmental interest
[20]. The proposed reactive species, Cl
2
O and Cl
2
, were generally present at low
concentrations but were shown to play a greater role than HOCl in the chlori-
nation process.
Table 3.1 reports the second-order rate constants for the chlorination of
amino acids and peptides [21-32]. Met and Cys reacted most rapidly with
chlorine (
k
> 10
7
/M/s). Aromatic acids, with the exception of Tyr, showed
reasonable reactivity (
k
∼ 10
4
-10
5
/M/s). Tyr had reactivity of the order of
10
1
/M/s. Ser and lys reacted similarly. Arg, Asn, and gln showed the lowest
reactivity (
k
∼ 10
−2
-10
1
/M/s). The rate constants for the chlorination of
gly, Ala, β-Ala, Val, and
iso
-leu were on the order of 10
4
-10
5
/M/s, similar to
the observed rate constants for basic aliphatic amines [19]. The order of
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