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Published online 9 August 2006
Published in J Environ Qual 35:1756-1763 (2006)
DOI: 10.2134/jeq2005.0410
© 2006 American Society of Agronomy, Crop Science Society of America, and Soil Science Society of America
677 S. Segoe Rd., Madison, WI 53711 USA
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Use of Beryllium-7 to Document Soil Redistribution following Forest Harvest Operations

Paulina Schullera, Andrés Irouméb, Desmond E. Wallingc,*, Héctor B. Mancillab, Alejandra Castilloa and Rosa E. Trumpera

a Facultad de Ciencias, Universidad Austral de Chile, Casilla 567, Valdivia, Chile
b Facultad de Ciencias Forestales, Universidad Austral de Chile, Casilla 567, Valdivia, Chile
c Department of Geography, University of Exeter, Amory Building, Rennes Drive, Exeter EX4 4RJ, UK


Figure 1
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Fig.1. Daily precipitation totals for the study period and the preceding month (A) and hourly precipitation totals for the period with maximum rainfall intensities (B).

 

Figure 2
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Fig. 2. The linear regression between the natural logarithm of the 7Be areal activity density and mass depth derived for the reference site.

 

Figure 3
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Fig. 3. The vertical distribution of 7Be at the reference site. (A) A plot of the mass activity density versus mass depth. (B) The reduction of the areal activity density with increasing mass depth.

 

Figure 4
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Fig. 4. The spatial distribution of the soil erosion (negative values) and sedimentation (positive values), kg m–2, along the slope transects of the study site. The decimal point of each number coincides with the position of the corresponding sampling point. The dashed lines represent contour lines. (A) Soil redistribution values determined using the 7Be approach, and (B) those obtained from the erosion pins.

 





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