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Fig. 7 Changes in the
fluorescence intensities of the
fluorophores regarding peak
A- ( a ) and C-( b ) regions with
solution pH for bulk sample
collected from Rio Solimoes
in Amazon basin rivers. The
error bar indicates their
standard deviation. Data
source Patel-Sorrentino et al.
( 2002 )
Peak A
Peak C
pH
3.6 pH
The fluorescence properties of various FDOM components are significantly
changed by pH variations (2-12) in aqueous solution (Figs. 6 , 7 , 8 ) (Gosh and
Schnitzer 1980 ; Henderson et al. 2009 ; Zhang et al. 2010 ; Laane 1982 ; Vodacek
and Philpot 1987 ; Pullin and Cabaniss 1995 ; Mobed et al. 1996 ; Patel-Sorrentino
et al. 2002 ; Baker et al. 2007 ; Spencer et al. 2007 ). The fluorescence intensities
at peak C- and peak A-regions for fulvic acid in Amazon basin rivers are signifi-
cantly increased up to pH 11, and then decrease in the pH interval 11-12 (Fig. 7 )
(Patel-Sorrentino et al. 2002 ). The ratios of fluorescence intensities of peak A and
peak C are independent of the molecular fractions of particulate (>0.22 μ m), col-
loidal and dissolved (<5 kDa) organic matter in natural waters (Patel-Sorrentino et
al. 2002 ). The fluorescence intensity of peak C (Ex/Em = 320-340/410-430 nm,
presumably caused by fulvic acid) is increased markedly between pH 2 and 6 and
then decreases at pH 8-10. In contrast, the fluorescence of peak C (Ex/Em = 370-
390/460-480 nm, possibly caused by humic acid) is unaltered at higher pH
(Henderson et al. 2009 ; Spencer et al. 2007 ).
In the case of bulk lake DOM, the autochthonous fulvic acids (C-like and
M-like, respectively, of algal origin) identified by PARAFAC modeling are
detected at pH 8-10, but the C-like component is absent at pH 2-4 (Fig. 8 )
(Mostofa KMG et al., unpublished data). The fluorescence intensities of the
M-like component are significantly influenced by pH in the peak A-region: com-
pared to the initial lake-water pH (7.5), a 79 % increase is observed at pH 2, it
decreases to 59 % at pH 4 and then gradually increases to 88 % at pH 10. The
 
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