Environmental Engineering Reference
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peroxide radicals with organic substances in aqueous solution (Mill et al. 1980 ;
Mageli and Kolczynski 1966 ; Faust and Hoigne 1987 ; Blough 1988 ; Kieber and
Blough 1990 ; Sakugawa et al. 1990 ; Faust and Allen 1992 ; Mostofa and Sakugawa
2009 ). Furthermore, the thermal decomposition of organic peroxides can initiate
the polymerization of vinyl monomers or induce cross-linking of a polymeric sub-
strate upon formation of free radical sites on the polymer (Mageli and Kolczynski
1966 ). The overall (unspeciated) photostationary-state concentration of peroxyl
radicals in sunlit cloud and fog waters is around 1-30 nM (Faust and Allen 1992 ).
The superoxide radical anion (O 2
- ) is the one-electron reduction product
of molecular oxygen. It is an early photoinduced and short-lived intermediate
that is formed in chemical reactions occurring in natural waters, where oxy-
gen acts as the ultimate electron acceptor (Jeong and Yoon 2005 ; Bielski et al.
1985 ; Petasne and Zika 1987 ; Zafiriou 1990 ; Micinski et al. 1993 ; Zafiriou et al.
1998 ; Millington and Maurdev 2004 ). It has been shown that the photoinduced
superoxide production rates are 0.1-6.0 nM min -1 under full-sun irradiation in
spring, and 0.2-8.0 nM min -1 in fall in a variety of Eastern Caribbean waters
(Micinski et al. 1993 ). A key reaction of O 2
- is the production of H 2 O 2 by dis-
mutation; hydrogen peroxide is then able to generate HO by direct photolysis or
upon photo-Fenton type reactions in sunlit aqueous solutions (Cooper et al. 1988 ;
Micinski et al. 1993 ; Fischer et al. 1985 ). Interestingly, the organic complexes of
Cu as well as the copper-catalyzed dismutation (involving Cu + and Cu 2 + ) can be
significant sinks of photoproduced O 2
- in seawater (Zafiriou et al. 1998 ; Voelker
et al. 2000 ).
The carbon dioxide radical anion (CO 2
- ) is a short-lived and highly reac-
tive intermediate that is photolytically formed in the ferrioxalate reaction sys-
tem. It is a strong oxidizing agent that is able to oxidize metals and other
chemical species in aqueous solution. The CO 2
- is formed photolytically (C 2 O 4
-
+ CO 2 ; k = 2 × 10 6 s -1 ) upon decomposition of the oxalyl radical
anion (C 2 O 4
CO 2
- ). The latter is produced by the photoinduced decomposition of the
highly photosensitive ferrioxalate complex [Fe(C 2 O 4 ) 3 ] 3- in aqueous solution
(Hislop and Bolton 1999 ; Jeong and Yoon 2004 , 2005 ; Mulazzani et al. 1986 ). A
key role played by CO 2
- is its ability to oxidize the metal ions, therefore affecting
the biogeochemical cycling of metal-containing species. These processes can have
an impact on the generation of HO
and of the superoxide radical anion in natural
waters (Hislop and Bolton 1999 ; Jeong and Yoon 2004 , 2005 ; Wang et al. 2010 ).
Another potentially important process is the transformation of organic substances
induced by CO 2
- , which is formed photolytically from ferrioxalate complexes in
the aqueous solution (Huston and Pignatello 1996 ).
In addition, it has been reported that quinones photolytically produce species capa-
ble of hydroxylation (Alegria et al. 1997 ; Pochon et al. 2002 ; Gan et al. 2008 ; Maurino
et al. 2008 ; Maddigapu et al. 2010 ; Page et al. 2011 ). Some of these quinone-derived
hydroxylating species exhibit reactivity that is around one order of magnitude lower
than free HO
(Pochon et al. 2002 ; Gan et al. 2008 ). It is hypothesized that quinone-
derived hydroxylating species may contribute at least in part to the photoinduced HO
production by DOM (Vaughn and Blough 1998 ; Page et al. 2011 ).
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