Environmental Engineering Reference
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by increasing the concentration of the catalase enzyme. The diurnal periodicity of
catalase activity matched the diurnal changes of H 2 O 2 (Clark et al. 2008 ; Angel et
al. 1999 ). The effects of H 2 O 2 and peroxides can be particularly important during
the summer season when their levels are higher. Moreover, ozone hole events in
Antarctic waters may greatly increase photodegradation processes that can gener-
ate reactive free radicals and peroxides, with a damaging influence on biogeochem-
ical cycles in Antarctic waters (Diffey 1991 ; Smith et al. 1992 ; Randall et al. 2005 ).
6.4 Impacts of H 2 O 2 on Microbial Quality of Recreational
Bathing Waters
Microbial water quality is assessed from the concentration of fecal indicator bacteria
(FIB) because of their adverse health effects (Cabelli et al. 1979 ; US Environmental
Protection Agency 2000 ; Wade et al. 2003 . Frequent FIB contamination episodes in
the surf zone resulted in multiple beach closures in the USA (Boehm et al. 2002 ). It is
shown that elevated levels of H 2 O 2 , ROOH, superoxide (O 2 ) and hydroxyl radical,
photolytically produced, can cause damage and cell lysis in microorganisms. This
may result into high FIB mortality in recreational bathing waters (Gonzalez-Flecha
and Demple 1997 ; Weinbauer and Suttle 1999 ; Mitchell and Chamberlin 1975 ; Clark
et al. 2008 ). It is estimated that approximately ~100 nM of H 2 O 2 can cause oxidative
stress to bacteria in waters (Angel et al. 1999 ). Diurnal cycles of FIB mortality in the
surf zone (Clark et al. 2008 ; Boehm et al. 2002 ), which well resemble the diurnal
cycle of H 2 O 2 , suggest that the FIB mortality may be linked to the photoinduced gen-
eration of H 2 O 2 and ROOH in sunlit surface waters.
7 Role of H 2 O 2 in the Origin of Autochthonous DOM
and of other Oxidising Agents
H 2 O 2 can contribute to the production of autochthonous DOM by different impor-
tant processes. First, it is involved in the photosysthesis process that is a major
source of organic matter (e.g. algae) (Mostofa et al. 2009a , b ). The photoinduced
and microbial assimilation of organic matter, including algae, can produce autoch-
thonous DOM in natural waters (Mostofa et al. 2009b ; Fu et al. 2010 ; Harvey
et al. 1995 ; Carrillo et al. 2002 ; Coble 2007 ; Yamashita and Tanoue 2004 ;
Yamashita and Tanoue 2008 ). Coherently, a correlation has been observed between
production of organic carbon and concentration of photolytically formed H 2 O 2
(Anesio et al. 2005 ). The autochthonous production of DOM (Mostofa et al. 2005 ;
Yoshioka et al. 2002 ) is typically observed during the summer season, and a major
DOM component that is produced is autochthonous fulvic acid, often termed
sedimentary fulvic acid (Hayase and Tsubota 1985 ). Other produced compounds
include marine humic substances (Coble 1996 , 2007 ), carbohydrates and unknown
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