Mercury budget of an upland-peatland watershed

被引:104
作者
Grigal, DF [1 ]
Kolka, RK [1 ]
Fleck, JA [1 ]
Nater, EA [1 ]
机构
[1] Univ Minnesota, Dept Soil Water & Climate, St Paul, MN 55108 USA
关键词
atmospheric deposition; litterfall; mercury cycling; wetland; throughfall;
D O I
10.1023/A:1006322705566
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Inputs, outputs, and pool sizes of total mercury (Hg) were measured in a forested 10 ha watershed consisting of a 7 ha hardwood-dominated upland surrounding a 3 ha conifer-dominated peatland. Hydrologic inputs via throughfall and stemflow, 13 +/- 0.4 mu g m(-2) yr(-1) over the entire watershed, were about double precipitation inputs in the open and were significantly higher in the peatland than in the upland (19.6 vs. 9.8 mu g m(-2) yr(-1)). Inputs of Hg via litterfall were 12.3 +/- 0.7 mu g m(-2) yr(-1), not different in the peatland and upland (11.7 vs. 12.5 mu g m(-2) yr(-1)). Hydrologic outputs via streamflow were 2.8 +/- 0.3 mu g m(-2) yr(-1) and the contribution from the peatland was higher despite its smaller area. The sum of Hg inputs were less than that in the overstory trees, 33 +/- 3 mu g m(-2) above-ground, and much less than either that in the upland soil, 5250 +/- 520 mu g m(-2), or in the peat, 3900 +/- 100 mu g m(-2) in the upper 50 cm. The annual flux of Hg measured in streamflow and the calculated annual accumulation in the peatland are consistent with values reported by others. A sink for Hg of about 20 mu g m(-2) yr(-1) apparently exists in the upland, and could be due to either or both storage in the soil or volatilization.
引用
收藏
页码:95 / 109
页数:15
相关论文
共 54 条
[1]   OCCURRENCE AND TRANSPORT OF MERCURY WITHIN A SMALL CATCHMENT-AREA [J].
AASTRUP, M ;
JOHNSON, J ;
BRINGMARK, E ;
BRINGMARK, L ;
IVERFELDT, A .
WATER AIR AND SOIL POLLUTION, 1991, 56 :155-167
[2]   Seasonal influences on partitioning and transport of total and methylmercury in rivers from contrasting watersheds [J].
Babiarz, CL ;
Hurley, JP ;
Benoit, JM ;
Shafer, MM ;
Andren, AW ;
Webb, DA .
BIOGEOCHEMISTRY, 1998, 41 (03) :237-257
[3]  
Benoit J. M., 1994, P187
[4]   DETERMINATION OF MERCURY IN SEAWATER AT SUB-NANOGRAM PER LITER LEVELS [J].
BLOOM, NS ;
CRECELIUS, EA .
MARINE CHEMISTRY, 1983, 14 (01) :49-59
[5]  
BOELTER DH, 1977, NC31 USDA FOR SERV N
[6]   THE ROLE OF DISSOLVED ORGANIC-CARBON IN THE CHEMISTRY AND BIOAVAILABILITY OF MERCURY IN REMOTE ADIRONDACK LAKES [J].
DRISCOLL, CT ;
BLETTE, V ;
YAN, C ;
SCHOFIELD, CL ;
MUNSON, R ;
HOLSAPPLE, J .
WATER AIR AND SOIL POLLUTION, 1995, 80 (1-4) :499-508
[7]   The case for atmospheric mercury contamination in remote areas [J].
Fitzgerald, WF ;
Engstrom, DR ;
Mason, RP ;
Nater, EA .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 1998, 32 (01) :1-7
[8]   ATMOSPHERIC CYCLING AND AIR-WATER EXCHANGE OF MERCURY OVER MIDCONTINENTAL LACUSTRINE REGIONS [J].
FITZGERALD, WF ;
MASON, RP ;
VANDAL, GM .
WATER AIR AND SOIL POLLUTION, 1991, 56 :745-767
[9]  
Fleck J.A., 1999, THESIS U MINNESOTA S
[10]   Mercury uptake by trees: An observational experiment [J].
Fleck, JA ;
Grigal, DF ;
Nater, EA .
WATER AIR AND SOIL POLLUTION, 1999, 115 (1-4) :513-523