Phosphate and tritium transport through undisturbed subsoil as affected by ionic strength

被引:28
作者
Jensen, MB
Hansen, HCB
Hansen, S
Jorgensen, PR
Magid, J
Nielsen, NE
机构
[1] Royal Vet & Agr Univ, Dept Agr Sci, Lab Soil Fertil & Plant Nutr, DK-1871 Frederiksberg, Denmark
[2] Royal Vet & Agr Univ, Dept Chem, DK-1871 Frederiksberg, Denmark
[3] Danish Geotech Inst, DK-2800 Lyngby, Denmark
关键词
D O I
10.2134/jeq1998.00472425002700010020x
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Storm flow can cause serious subsurface losses of dissolved orthophosphate from soils that under low now conditions effectively retain orthophosphate (P-i). To test if storm flow loss of P-i can be related to preferential flow and/or decrease in ionic strength of mobile solution we applied combined pulses of (H2PO4-)-P-32 ((32)p) and tritium ((H2O)-H-3) to an undisturbed column of clayey subsoil (diam, 0.5 m, height 0.73 m) subjected to water saturated steady flow, with either distilled water (0.003 mS cm(-1)) or a dilute salt solution (0.2 mS cm(-1)). The pulse applications resulted in narrow breakthroughs of P-32 with peak arrivals after displacement of only 2 to 4% of the total water content. In comparison, the (H2O)-H-3-breakthrough curves had peak arrivals after displacement of 8 to 18% of the total water content and showed extensive tailing, In distilled water approximately twice as much phosphate was transported through the column than in the diluted salt solution, although the recovery percentage in both cases was <1% of the applied P-32-mass. Slicing of the column after dye application confirmed the presence of heterogeneous flow paths, The results suggest that the positive correlation observed between concentration of dissolved Pi and field effluent discharge rate is restricted to rainfall intensities that initiate preferential flow, and that the P-i-transport is increased the more dilute the percolating solution remains.
引用
收藏
页码:139 / 145
页数:7
相关论文
共 53 条
[1]  
ANDERSEN HE, 1994, 120 DMU NATL ENV RES
[2]   NEW CULTURE-MEDIUM CONTAINING IONIC CONCENTRATIONS OF NUTRIENTS SIMILAR TO CONCENTRATIONS FOUND IN THE SOIL SOLUTION [J].
ANGLE, JS ;
MCGRATH, SP ;
CHANEY, RL .
APPLIED AND ENVIRONMENTAL MICROBIOLOGY, 1991, 57 (12) :3674-3676
[3]   MACROPORES AND WATER-FLOW IN SOILS [J].
BEVEN, K ;
GERMANN, P .
WATER RESOURCES RESEARCH, 1982, 18 (05) :1311-1325
[4]   THE INFLUENCE OF IRON-OXIDES ON PHOSPHATE ADSORPTION BY SOIL [J].
BORGGAARD, OK .
JOURNAL OF SOIL SCIENCE, 1983, 34 (02) :333-341
[5]  
Bottcher A. B., 1985, Soil erosion and conservation, P622
[6]   USING MORPHOMETRIC EXPRESSIONS FOR MACROPORES TO IMPROVE SOIL PHYSICAL ANALYSES OF FIELD SOILS [J].
BOUMA, J .
GEODERMA, 1990, 46 (1-3) :3-11
[7]  
BOUMA J, 1991, ADV AGRON, V46, P1
[8]   The hydrometer as a new method for the mechanical analysis of soils [J].
Bouyoucos, GJ .
SOIL SCIENCE, 1927, 23 (05) :343-353
[9]   MODELING THE TRANSPORT OF SOLUTES INFLUENCED BY MULTIPROCESS NONEQUILIBRIUM [J].
BRUSSEAU, ML ;
JESSUP, RE ;
RAO, PSC .
WATER RESOURCES RESEARCH, 1989, 25 (09) :1971-1988
[10]   Organic phosphorus in solutions and leachates from soils treated with animal slurries [J].
Chardon, WJ ;
Oenema, O ;
delCastilho, P ;
Vriesema, R ;
Japenga, J ;
Blaauw, D .
JOURNAL OF ENVIRONMENTAL QUALITY, 1997, 26 (02) :372-378