Tạp chí Hóa học, 54(5): 591-596, 2016<br />
DOI: 10.15625/0866-7144.2016-00370<br />
<br />
c<br />
1*<br />
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T<br />
<br />
, Bjarne W. Strowble2<br />
<br />
1<br />
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2<br />
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3<br />
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Hàn lâm Khoa h<br />
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Đến Tòa soạn 22-12-2015; Chấp nhận đăng 25-10-2016<br />
Abstract<br />
Elements release from initial soil column into flooding water was studied under oxidized and reduced condition,<br />
and combining with added dissolve organic carbon in flooding water. When dissolve organic carbon presented in<br />
flooding water, element release as Cr, Pb, Ni, As, Co, Al, Cu were increased in both under condition oxidized and<br />
reduced. Pb, As, Co and Sb release were highest under reduced condition comparing under oxidized condition,<br />
meanwhile, meanwhile Cr, Cu and Al release were highest under oxidized condition.<br />
Keywords. Release of elements, rice field, dissolve organic carbon, flooding water.<br />
<br />
[1]<br />
<br />
T<br />
<br />
[2],<br />
(DOC) [3].<br />
<br />
-4<br />
<br />
o<br />
<br />
[4-7].<br />
2-<br />
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4<br />
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aldrich. HNO3 (Baker Instra).<br />
<br />
[8].<br />
Tisted Nørskov, Na Uy theo Strobel [12]<br />
<br />
[9-11].<br />
<br />
1/4<br />
2∙2H2O;<br />
<br />
591<br />
<br />
15 mg MgSO4∙7H2O;<br />
<br />
TCHH, 54(5) 2016<br />
<br />
Trịnh Thu Hà và cộng sự<br />
<br />
16,2 mg NaHCO3<br />
<br />
-<br />
<br />
% N2<br />
<br />
%<br />
<br />
H2<br />
tinh (Metrohm, 6.0228.000).<br />
(COY Vinyl Anaerobic Chamber<br />
TG-Instrument AB<br />
<br />
2<br />
<br />
type<br />
<br />
B,<br />
qua 1 đêm<br />
<br />
20±1 oC trong<br />
<br />
(Metrohm, 6.0228.000).<br />
<br />
đ [13-15].<br />
<br />
sâu 1<br />
<br />
th<br />
3<br />
<br />
o<br />
<br />
C.<br />
<br />
592<br />
<br />
TCHH, 54(5) 2016<br />
<br />
D<br />
<br />
[4, 5, 7].<br />
[20]<br />
Mn(OH)2<br />
<br />
2<br />
<br />
tăng<br />
h<br />
<br />
2<br />
<br />
au 72<br />
<br />
Mn(OH)2 [16-19]<br />
<br />
d) Cu<br />
<br />
a) Al<br />
72<br />
<br />
i gian (g )<br />
<br />
i gian (g )<br />
<br />
72<br />
<br />
48<br />
<br />
48<br />
<br />
24<br />
<br />
24<br />
0<br />
<br />
0.08<br />
ng n ng đ<br />
<br />
0<br />
<br />
0.16<br />
0.24<br />
a g i (mg/kg)<br />
72<br />
<br />
i gian (g )<br />
<br />
i gian (g )<br />
<br />
0.01<br />
0.015<br />
a g i (mg/kg)<br />
e) Pb<br />
<br />
b) Fe<br />
72<br />
<br />
48<br />
<br />
48<br />
<br />
24<br />
<br />
24<br />
0<br />
<br />
40<br />
ng n ng đ<br />
<br />
0<br />
<br />
80<br />
120<br />
a g i (mg/kg)<br />
<br />
0.001<br />
ng n ng đ<br />
<br />
0.002<br />
0.003<br />
a g i (mg/kg)<br />
f) Ni<br />
<br />
c) Mn<br />
<br />
72<br />
<br />
i gian (g )<br />
<br />
72<br />
<br />
i gian (g )<br />
<br />
0.005<br />
ng n ng đ<br />
<br />
48<br />
<br />
48<br />
<br />
24<br />
<br />
24<br />
0<br />
DOC:0 mg/L<br />
<br />
12<br />
ng n ng đ<br />
DOC:5 mg/L<br />
<br />
0<br />
<br />
24<br />
36<br />
a g i (mg/kg)<br />
DOC:25 mg/L<br />
<br />
593<br />
<br />
Đ u<br />
<br />
0.005<br />
ng n ng đ<br />
n<br />
<br />
Đ u<br />
<br />
0.01<br />
0.015<br />
a g i (mg/kg)<br />
n<br />
<br />
-DOC:25 mg/L<br />
<br />
TCHH, 54(5) 2016<br />
<br />
Trịnh Thu Hà và cộng sự<br />
72<br />
<br />
72<br />
<br />
b) DOC<br />
<br />
i gian (g )<br />
<br />
i gian (g )<br />
<br />
a) pH<br />
48<br />
<br />
24<br />
<br />
48<br />
<br />
24<br />
6.0<br />
<br />
6.5<br />
<br />
7.0<br />
<br />
7.5<br />
<br />
0<br />
<br />
25<br />
50<br />
75<br />
DOC (mg/l)<br />
<br />
pH<br />
<br />
100<br />
<br />
72<br />
<br />
72<br />
<br />
d) Cr<br />
<br />
i gian (g )<br />
<br />
i gian (g )<br />
<br />
c) Fe(II)<br />
48<br />
<br />
48<br />
<br />
24<br />
<br />
24<br />
0<br />
<br />
25<br />
50<br />
ng n ng đ<br />
<br />
DOC:0 mg/L<br />
<br />
0<br />
<br />
75<br />
100<br />
a g i (mg/kg)<br />
<br />
DOC:5 mg/L<br />
<br />
0.0025<br />
ng n ng đ<br />
<br />
Đ u<br />
<br />
DOC:25 mg/L<br />
<br />
n<br />
<br />
0.005<br />
0.0075<br />
a g i (mg/kg)<br />
<br />
Đ u<br />
<br />
n<br />
<br />
a) As<br />
72<br />
<br />
i gian (g )<br />
<br />
i gian (g )<br />
<br />
-DOC:25 mg/L<br />
<br />
b) Co<br />
<br />
72<br />
<br />
48<br />
<br />
24<br />
0<br />
<br />
24<br />
0<br />
<br />
c) Sb<br />
<br />
i gian (g )<br />
<br />
24<br />
0.001<br />
ng n ng đ<br />
<br />
DOC:0 mg/L<br />
<br />
d) Zn<br />
<br />
48<br />
<br />
24<br />
0<br />
<br />
0.002<br />
0.003<br />
a g i (mg/kg)<br />
<br />
DOC:5 mg/L<br />
<br />
0.01 0.02 0.03 0.04 0.05<br />
ng n ng đ<br />
a g i (mg/kg)<br />
<br />
72<br />
<br />
48<br />
<br />
0<br />
<br />
48<br />
<br />
0.02 0.04 0.06 0.08<br />
ng n ng đ<br />
a g i (mg/kg)<br />
<br />
72<br />
<br />
i gian (g )<br />
<br />
125<br />
<br />
DOC:25 mg/L<br />
<br />
594<br />
<br />
Đ u<br />
<br />
0.15<br />
ng n ng đ<br />
n<br />
<br />
Đ u<br />
<br />
0.3<br />
0.45<br />
a g i (mg/kg)<br />
n<br />
<br />
-DOC:25 mg/L<br />
<br />
TCHH, 54(5) 2016<br />
[21].<br />
<br />
.<br />
<br />
[6, 22-25]<br />
[12]<br />
<br />
, mã<br />
số 10.PO4.VIE.<br />
><br />
<br />
1.<br />
<br />
I. Kögel-Knabner , W. Amelung, Z. Cao, S. Fiedler,<br />
P. Frenzel, R. Jahn. Biogeochemistry of paddy soils,<br />
Geoderma, 157(1-2), 1-14 ( 2010).<br />
<br />
2.<br />
<br />
T. Borch, R. Kretzschmar, A. Kappler, P. V.<br />
Cappellen, M. Ginder-Vogel, A. Voegelin.<br />
Biogeochemical Redox Processes and their Impact<br />
on Contaminant Dynamics, Environmental Science &<br />
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<br />
3.<br />
<br />
J. Luo, M. Ma, C. Liu, J. Zha, Z. Wang. Impacts of<br />
particulate organic carbon and dissolved organic<br />
carbon on removal of polycyclic aromatic<br />
hydrocarbons, organochlorine pesticides, and<br />
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180-187 (2009).<br />
<br />
4.<br />
<br />
G. Tyler. Leaching of metals from the A-horizon of a<br />
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<br />
5.<br />
<br />
N. V. Hue, G. R. Craddock, F. Adams. Effect of<br />
Organic Acids on Aluminum Toxicity in Subsoils1,<br />
Soil Sci. Soc Am. J., 50(1), 28-34 (1986).<br />
<br />
6.<br />
<br />
D. Berggren. Speciation of copper in soil solutions<br />
from podzols and cambisols of S. Sweden, Water Air<br />
Soil Pollut, 62(1-2), 111-123 (1992).<br />
<br />
7.<br />
<br />
A. A. Pohlman, J. G. McColl. Soluble Organics from<br />
Forest Litter and their Role in Metal Dissolution,<br />
Soil Sci Soc Am J, 52(1), 265-271 (1988).<br />
<br />
8.<br />
<br />
J. Murase, M. Kimura. Anaerobic reoxidation of<br />
Mn2+, Fe2+, S0 and S2– in submerged paddy soils, Biol<br />
Fertil Soils, 25(3), 302-306 (1997).<br />
<br />
9.<br />
<br />
F. Amery, F. Degryse, W. Degeling, E. Smolders, R.<br />
Merck.<br />
The<br />
Copper-Mobilizing-Potential<br />
of<br />
Dissolved Organic Matter in Soils Varies 10-Fold<br />
Depending on Soil Incubation and Extraction<br />
Procedures, Environmental Science & Technology,<br />
41(7), 2277-2281 (2007).<br />
<br />
[20].<br />
<br />
[28].<br />
<br />
3<br />
3<br />
<br />
H2AsO4-, H2AsO42-<br />
<br />
6<br />
<br />
[28]<br />
<br />
Ca<br />
<br />
10. G. F. Koopmans, J. E. Groenenberg. Effects of soil<br />
oven-drying on concentrations and speciation of<br />
trace metals and dissolved organic matter in soil<br />
solution extracts of sandy soils, Geoderma, 161(3-4),<br />
147-158 (2011).<br />
11. Y. L. Phyu, M. S. J. Warne, R. P. Lim. Toxicity and<br />
bioavailability of atrazine and molinate to the<br />
freshwater fish (Melanotenia fluviatilis) under<br />
laboratory and simulated field conditions, Sci. Total<br />
Environ., 356(1-3), 86-99 (2006).<br />
<br />
595<br />
<br />