Impact of isostatic uplift and ditching of sulfidic sediments on the hydrochemistry of major and trace elements and sulfur isotope ratios in streams,western Finland

Citation
M. Astrom et B. Spiro, Impact of isostatic uplift and ditching of sulfidic sediments on the hydrochemistry of major and trace elements and sulfur isotope ratios in streams,western Finland, ENV SCI TEC, 34(7), 2000, pp. 1182-1188
Citations number
30
Categorie Soggetti
Environment/Ecology,"Environmental Engineering & Energy
Journal title
ENVIRONMENTAL SCIENCE & TECHNOLOGY
ISSN journal
0013936X → ACNP
Volume
34
Issue
7
Year of publication
2000
Pages
1182 - 1188
Database
ISI
SICI code
0013-936X(20000401)34:7<1182:IOIUAD>2.0.ZU;2-H
Abstract
Acid soil drainage is of major economic concern for the arable crop farmers and fishermen in midwestern Finland. Almost all the farmland in this regio n consist of acid sulfate soils developed on sulfide-bearing fine-grained m arine and lacustrine sediments. During rain storms in autumn and snowmelt i n spring these soils are flushed, resulting in low pH and high metal concen trations in affected watercourses. A study of 40 first- and second-order st reams during the 1997 autumn high water flow event demonstrated that (1) th e pH in peat/till dominated catchments is controlled by organic acids (pH > 4.5), while in streams draining acid sulfate soil pH is controlled by sulf uric acid (4.5 > pH > 3.0); (2) the delta(34)S((sulfate)) values with range of -16 to +7 parts per thousand VCDT show two populations with medians of -6.2 and +3.2 parts per thousand, the first is dominated by original sedime ntary sulfide and the second is most likely related to secondary sulfide fo rmation in the acid sulfate soils; (3) the concentrations of Al, Ca, Cd, Cl , Co, Cu, Mn, Ni, Na, Zn, and SO42- are considerably higher in streamwaters in the investigated area than in headwater streams from the whole country as a result of extensive leaching of the acid sulfate soils; and (4) As, Ba , Cr, Fe, Ph, Sb, and V concentrations are controlled by soil and water pH, dissolved organic matter, and suspended particles and are not like the oth er trace elements, significantly enriched in the streamwaters.