Soil Science Society of America Journal
Soil Sci. Soc. Am. J. 78:1753–1764
doi:10.2136/sssaj2013.12.0511
Received 5 Dec. 2013.
*Corresponding author (pascal.podwojewski@ird.fr).
© Soil Science Society of America, 5585 Guilford Rd., Madison WI 53711 USA
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How Tree Encroachment and Soil Properties Affect Soil
Aggregate Stability in an Eroded Grassland in South Africa
Forest, Range & Wildland Soils
T
he management of natural grasslands has received much attention glob-
ally due to their importance in providing grazing for livestock. Natural
grasslands account for 40% of the earth land-surface and almost 1 ´ 10
9
people utilize them (White et al., 2000). Any degradation of grasslands is likely to
have a negative impact on local human populations, especially on rural livestock-
dependent communities.
Tree (or bush) encroachment in climax grasslands is a widespread phenomenon
and has been observed for over 140 yr (Van Auken, 2009) in diferent regions of the
world (e.g., America, Australia, Africa, and Southeast Asia; Archer et al., 2001). Trees
in grassland ecosystems have large impacts on grassland ecology and dynamics and es-
pecially on water resources and soil surface features. In grasslands of semiarid areas, tree
encroachment has been correlated to higher runof that generates higher inter-rill ero-
sion associated with reduced grass cover under trees (Petersen and Stringham, 2008).
Te presence of trees is also linked to an increase of evapotranspiration (Scott et al.,
Pascal Podwojewski*
IRD UMR 242 IEES-Paris
c/o School of Agriculture
Earth and Environmental Science
Univ. of KwaZulu-Natal
Box X01
Scottsville, 3209
South Africa
and
IRD UMR 242 IEES-Paris
32 Ave. H. Varagnat
93143 Bondy cedex
France
Séraphine Grellier
IRD UMR 242 IEES-Paris c/o School of
Agriculture
Earth and Environmental Science
Univ. of KwaZulu-Natal
Box X01
Scottsville, 3209
South Africa
and
Univ. of Science and
Technology of Hanoi
Vietnam
Sandile Mthimkhulu
School of Agriculture, Earth and
Environ. Science
Univ. of KwaZulu-Natal
Box X01
Scottsville, 3209
South Africa
Louis Titshall
School of Agriculture, Earth School of
Agriculture, Earth and
Environ. Science
Univ. of KwaZulu-Natal
Box X01
Scottsville, 3209
South Africa
and
Inst. for Commercial Forestry Research
P.O. Box 100281
Scottsville, 3209
South Africa
Gully erosion and woody plant encroachment are frequently observed in
grasslands worldwide. Soil aggregate stability is one of the drivers of gul-
ly erosion and needs to be studied, especially in the context of both tree
encroachment and gully erosion. This study compared the effects of tree
encroachment [paperbark thorn; Vachellia sieberiana (DC.) Kyal. & Boatwr.
previously called Acacia sieberiana DC.] and soil surface horizon properties
on the aggregate stability (as measured by mean weight diameter, MWD) in
a degraded semihumid grassland in the KwaZulu-Natal province of South
Africa. Soil properties from under trees (UT) and open areas (OA) of both an
Entisol within deep gullies (locally called dongas) and Alfsol from grasslands
outside the gullies (grassland). The MWD values were higher in the grassland
(3.06 ± 0.21 mm) than in the dongas (1.84 ± 1.03 mm). In the grassland,
the MWD was signifcantly higher in the OA than UT, associated with more
fne roots in the OA. In the donga, soil properties UT were not signifcantly
different than those in OA. The soil aggregate stability showed strong local
variability that depends on the age of the donga and the nature of the mate-
rial that composes the pediments. Illite was associated with higher MWD
values. The presence of interstratifed illite–vermiculite located in active don-
ga increases the shrink–swell potential of the aggregates, exacerbating their
dispersion refected in the low MWD values measured, especially when C
and root contents were also low. These results suggest that the local soil clay
mineralogy controls the orientation and extension of gullies rather than soil
chemistry, topography, or the size of the drainage area.
Abbreviations: CEC, cation exchange capacity; MWD, mean weight diameter of
aggregates; OA, open area; PCA, principal components analysis; SW, soil water content;
UT, under trees; D
b
, bulk density.
Published August 22, 2014