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shorter wavelengths (Ex/Em = 295-310/443-450 nm) in surface waters (0-20 m)
compared to the deep water layers (40-80 m) (Ex/Em = 300-310/444-464 nm).
Furthermore, maxima are 320-325/422-454 nm in sea waters and 300-305/449
and 250/449 nm in irradiated river waters (Table 2 ) (Mostofa KMG et al., unpub-
lished data; Mostofa et al. 2005b ; Yamashita et al. 2011 ). The excitation-emis-
sion maxima of the fluorescence peak C are shifted in irradiated samples from
longer to shorter wavelength regions, which gives a blue-shift of the peak position
(Mostofa et al. 2005a , 2007a ; Moran et al. 2000 ). Such blue-shift phenomenon is
the photoinduced result of the mineralization of fluorophores that are present in
the molecular structure of fulvic acids. Irradiation decomposes the allochthonous
fulvic acid (A-like and M-like) entirely (Table 2 ) (Mostofa KMG et al., unpub-
lished data). Photobleached fulvic acid is generally detected in the surface waters
of rivers, lakes, estuaries and oceans (Table 2 ) (Brooks et al. 2007 ; Mostofa et al.
2007a , 2005b ; Garcia et al. 2005 ; Skoog et al. 1996 ; Moran et al. 2000 ; Osburn
et al. 2009 ; Lepane et al. 2003 ; Abboudi et al. 2008 ; Poiger et al. 1999 ; Zhang
et al. 2009b ).
Allochthonous Humic Acids (C-like, A-like and M-like )
The standard Suwannee River Humic Acid (SRHA) has three fluorescent com-
ponents, namely allochthonous humic acid (C-like), humic acid (A-like) and
humic acid (M-like). They can be identified using PARAFAC modeling of EEM
spectra in a variety of waters (Fig. 3 f, g; Table 2 ). The allochthonous humic acid
(C-like) shows three fluorescence peaks, of which two are at Ex/Em = 285-340/
460-480 nm (shorter wavelength) and at 350-405/480-508 nm (longer wavelength,
peak C-region). The third peak is located at Ex/Em = 240-270/460-508 nm in
the peak A-region (Fig. 3 f; Table 2 ). Allochthonous humic acid (C-like) has been
detected at Ex/Em = 320-350/461-498 and 300/461 nm (peak C-region) and
at 255/461 nm (peak A-region) in standard SRFA dissolved in Milli-Q water; at
295-310/423-464 and 255/464 nm in extracted humic acid; at 330/456-480 and
<250/450-460 nm in river and soil waters; at 385/>500 and 256/>500 nm in estu-
aries; at 300-340/>500-510, 290-405/>500-510 and <260-270/>508 nm in bay
and marine waters; at 370-380/490-498 and <260/490-498 nm in the north Pacific
and Atlantic ocean; at 360/458-480, 300/458 and 250-260/458-480 nm in drinking
water treatment plants and municipal wastes; at 370/440 and <250/440 nm in soil;
at 351/459 and 240/459 nm in water extracted from sugar maple leaves; finally, at
350-360/460-480 nm in plant biomass, manure and soil (Fig. 3 f; Table 2 ) (Coble
1996 ; Mostofa et al. 2005a ; Ohno and Bro 2006 ; Baker 2005 ; Hunt et al. 2008 ;
Kowalczuk et al. 2009 ; Baghoth et al. 2010 ; Chen et al. 2010 ; Fellman et al.
2008 , 2010 ; Guo et al. 2010 ; Yu et al. 2010 ; Wu et al. 2011 ; Yamashita et al. 2011 ;
Balcarczyk et al. 2009 ; Santín et al. 2009 ; Murphy et al. 2008 ; Yamashita and Jaffé
2008 ).
The allochthonous humic acid (A-like) can exhibit a strong shoulder (not
often a clear peak) at peak A-region in a wide range of emission wavelengths.
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