Jb. Christensen et al., CHARACTERIZATION OF THE DISSOLVED ORGANIC-CARBON IN LANDFILL LEACHATE-POLLUTED GROUNDWATER, Water research, 32(1), 1998, pp. 125-135
Samples of dissolved organic carbon (DOG) were obtained from landfill
leachate-polluted groundwater at Vejen Landfill, Denmark. The humic ac
ids, fulvic acids and the hydrophilic fraction were isolated and purif
ied. Based on DOC measurements, the fulvic acid fraction predominated,
accounting for about 60% of the total amount of DOC with an apparent
molecular weight of about 1800 Da. The hydrophilic fraction constitute
d about 30% of the total amount of DOC with an apparent molecular weig
ht of about 2100 Da, and the humic acid fraction made up about 10% of
the total amount of DOC with an apparent molecular weight of about 260
0 Da. The elemental compositions of the humic acids, fulvic acids and
the hydrophilic fraction were in the ranges typical for humic substanc
es from other origins. The O/C ratios for humic acids, fulvic acids an
d the hydrophilic fraction were similar in the leachate-polluted groun
dwater. For humic acids the O/C ratios were slightly higher than repor
ted in the literature, indicating a high content of carboxylic groups,
phenolic groups or carbohydrates. Acid-base titration indicated that,
in the fulvic acids and the hydrophilic fraction, carboxylic acids we
re the dominating functional group, representing about 6 meg g(-1). Th
e weakly acidic groups in fulvic acids and the hydrophilic fraction re
presented about 1 and 3 meg g(-1), respectively. The total acidity in
fulvic acids and the hydrophilic fraction accounted for 48-57% of the
O/C ratio. In the humic acids, carboxylic groups made up about 3 meg g
-(-1) and the weakly acidic groups made up about 1.5 meg g(-1). The to
tal acidity accounted for 29-32% of the O/C ratio. The characterizatio
n of DOC in leachate-polluted groundwater in terms of humic acids, ful
vic acids and hydrophilic fraction showed that the hydrophilic fractio
n resembles, in many ways, humic and fulvic acids; thus, a distinction
between the fractions may be related to the methods only and be of li
ttle practical value. The three fractions constituting the DOC content
in a sample should all be considered when evaluating processes such a
s metal complexation and transport of metals and hydrophobic, organic
contaminants. (C) 1998 Elsevier Science Ltd. All rights reserved.