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Global Change Abstracts The Swiss Contribution - SCNAT

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118<br />

separation were increased. Trafficking had no<br />

clear effect on the orientation of pores. While the<br />

mean pore diameter tended to decrease, biopores<br />

were more stable than interaggregate pores originating<br />

from the packing of soil aggregates. This<br />

is relevant for the development of structural stability<br />

in restored soils, as the macro-pores consist<br />

mainly of interaggregate pores initially, whereas<br />

biopores develop and increase in proportion only<br />

gradually over time. Quantitative morphometry<br />

provides valuable morphological indices for the<br />

objective assessment of the macro-pore structure<br />

and changes induced by compaction.<br />

European Journal of Soil Science, 2007, V58, N5,<br />

OCT, pp 1062-1073.<br />

08.1-212<br />

Reducing phosphorus losses from over-fertilized<br />

grassland soils proves difficult in the<br />

short term<br />

Schärer M, Stamm C, Vollmer T, Frossard E, Oberson<br />

A, Flühler H, Sinaj S<br />

Switzerland<br />

Water Resources , Agriculture, Soil Sciences , Toxicology<br />

, Hydrology<br />

Phosphorus (P) losses from many agricultural<br />

soils are driven by fast transport processes, such<br />

as surface runoff, shallow interflow and macropore<br />

flow. Close interaction of rain with topsoil layers<br />

(0-5 cm), rich in available P, results in high P<br />

concentrations in these rapid runoff pathways.<br />

This is particularly pronounced in permanent<br />

grassland soils typically characterized by a P enrichment<br />

of the topsoil. One option to mitigate P<br />

losses from grassland is therefore to reduce soil<br />

P content, particularly available P, in this critical<br />

surface layer. Omitting application of P fertilizer<br />

will reduce soil P in the long term but more drastic<br />

methods may be necessary to achieve P loss<br />

reductions in shorter time-scales. In this study,<br />

three management options to reduce P in runoff<br />

from grassland soils were evaluated in a field experiment<br />

lasting 2 years on two grassland sites: (i)<br />

no P inputs, (ii) no P inputs plus soil tillage and<br />

(iii) no P inputs plus tillage combined with application<br />

of a P sorbing soil amendment (iron oxide).<br />

Withholding P inputs did not decrease either the<br />

available P in the soil or the P concentrations in<br />

runoff from sprinkler experiments over a 2-year<br />

period. Both the treatments which included tillage<br />

caused immediate reductions in both soil<br />

available P and runoff P, with Fe/OH amendment<br />

being more effective. However, in the second year<br />

the effects of both tillage treatments were less apparent<br />

and only the Fe/OH treatment significantly<br />

decreased runoff P. <strong>The</strong> results indicate that the<br />

<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Soil and Lithosphere<br />

long-term enrichment of soils due to P application<br />

in excess of plant needs is unlikely to be remedied<br />

by short-term treatments. However, further<br />

work is required to assess the applicability of our<br />

conclusion to other sites.<br />

Soil Use and Management, 2007, V23, SEP, S1, pp<br />

154-164.<br />

08.1-213<br />

Heavy metal contamination along a soil<br />

transect in the vicinity of the iron smelter of<br />

Kremikovtzi (Bulgaria)<br />

Schulin R, Curchod F, Mondeshka M, Daskalova A,<br />

Keller A<br />

Switzerland, Bulgaria<br />

Agriculture, Soil Sciences , Toxicology , Geochemistry<br />

& Geophysics<br />

Based on previous preliminary survey results,<br />

elevated heavy metal concentrations of the agricultural<br />

soils of the villages of the Kremikovtzi<br />

region east of the Bulgarian capital Sofia were<br />

attributed to pollution from dusts emitted by<br />

the iron smelter in the centre of the region. Additional<br />

sampling in a test area indicated that<br />

high metal concentrations in this area could also<br />

be of geogenic origin. In order to test this hypothesis,<br />

we sampled a sequence of 14 soil profiles at<br />

increasing distance from the smelter along a 2<br />

km transect through agricultural land outside<br />

the metallurgical complex of Kremikovtzi. <strong>The</strong><br />

transect extended through two different units of<br />

soil types: Chromic Luvisols and Alluvial Fluvisols.<br />

Samples of the fine earth fraction (

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