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Agriculture, Ecosystems and Environment
journal homepage: www.elsevier.com/locate/agee
Trees increase soil organic carbon and nutrient availability in temperate
agroforestry systems
P. Pardon
a,b,c,
⁎
, B. Reubens
a
, D. Reheul
b
, J. Mertens
d
, P. De Frenne
b
, T. Coussement
e
, P. Janssens
e
,
K. Verheyen
c
a
Flanders Research Institute for Agriculture, Fisheries and Food (ILVO), Burgemeester Van Gansberghelaan 109, 9820 Merelbeke, Belgium
b
Department of Plant Production, Ghent University, Coupure Links 653, 9000 Ghent, Belgium
c
Department of Forest and Water Management, Ghent University, Geraardsbergsesteenweg 267, 9090 Gontrode, Belgium
d
Department of Applied Biosciences, Ghent University, Valentin Vaerwyckweg 1, 9000 Ghent, Belgium
e
Soil Service of Belgium, Willem de Croylaan 48, 3001 Leuven, Belgium
ARTICLE INFO
Keywords:
Alley cropping
Soil organic carbon
Soil fertility
Temperate agroforestry
Poplar
ABSTRACT
Agroforestry systems (AFS) have a large potential to deliver a wide range of ecosystem services (ES). In field and
crop management, changes to factors such as regulatory ES delivery are rarely taken into account, in part due to
the paucity of detailed quantification of how trees affect biophysical field characteristics. This is especially true
for arable systems in temperate climates. We have therefore assessed the influence of rows of trees of varying size
on the prevailing soil characteristics in arable AFS. Spatial variability of soil organic carbon, acidity and nutrient
status (N, P, K, Ca, Mg and Na) of the plough layer were analysed on a set of 17 arable agroforestry fields
comprising 6 young (< 5 years) alley cropping fields and 11 fields bordered by a row of trees of moderate to
older age (15–47 years) in Belgium. Significantly higher soil organic carbon and soil nutrient concentrations of
N, P, K, Mg and Na were observed in the vicinity of trees in field boundaries, most likely resulting from the input
of tree litter and nutrient-enriched throughfall water (for K and Na). Observed increases were strongly related to
the distance from the tree row, resulting in a gradual change in soil conditions up to at least 30 m into the field.
No significant effects of distance from the tree rows on soil characteristics were found in the young alley
cropping fields. These results highlight the potential of middle-aged to mature tree rows to increase soil organic
carbon stocks and nutrient availability for the agricultural crop in AFS.
1. Introduction
In temperate regions, interest in agroforestry has been growing for
20 years (Borremans et al., 2016; Gillespie et al., 2000; Jose et al.,
2004; Nair, 2007) because it is considered as a sustainable agricultural
practice that combines primary production with other ecosystem ser-
vices (ES) (Torralba et al., 2016). In this paper an AFS is defined as a
land use system in which trees are grown in combination with agri-
cultural crops, and where both ecological and economic interactions
occur between the tree and non-tree components of the system
(Oelbermann et al., 2004; Young, 1989). The tree component can be
located either inside the field (e.g. “alley cropping”), or on the field
edges (e.g. “boundary planting”)(Nair et al., 2009; Young, 1989).
Several authors have highlighted the potential beneficial effects of AFS
such as carbon sequestration (Cardinael et al., 2015a; Montagnini and
Nair, 2004), protection of (ground)water quality through reduction of
nitrogen leaching (Allen et al., 2004; Jose, 2009), mitigation of soil
erosion (Nair, 2007) and biodiversity conservation (Klaa et al., 2005).
However, in large parts of temperate Europe, implementation of agro-
forestry remains rather limited (Reisner et al., 2007; Rigueiro-
Rodríguez et al., 2009). Besides uncertainties on the legislative and
economic level (Borremans et al., 2016), this might result from a lack of
actual quantification of the ES provided and the lack of knowledge on
implications of AFS on field management (Graves et al., 2009;
Tsonkova et al., 2014).
Particularly in regions with oceanic and continental climatic con-
ditions (as defined by Peel et al. (2007)), further research and quanti-
fication is needed regarding the effect of tree presence on soil organic
carbon (SOC) (Cardinael et al., 2015a; Jose, 2009; Peichl et al., 2006)
and soil nutrient availability (Cardinael et al., 2015a; Jose, 2009; Jose
et al., 2000). For various AFS in the (sub-)tropical regions, the occur-
rence and magnitude of these effects on SOC (e.g. Albrecht and Kandji,
2003; Gupta et al., 2009) and soil nutrient content (e.g. Nair et al.,
1999; Szott et al., 1991) have already been thoroughly studied, where
http://dx.doi.org/10.1016/j.agee.2017.06.018
Received 26 January 2017; Received in revised form 7 June 2017; Accepted 11 June 2017
⁎
Corresponding author at: Department of Forest and Water Management, Ghent University, Geraardsbergsesteenweg 267, 9090 Gontrode, Belgium.
E-mail address: paul.pardon@ilvo.vlaanderen.be (P. Pardon).
Agriculture, Ecosystems and Environment 247 (2017) 98–111
0167-8809/ © 2017 Elsevier B.V. All rights reserved.
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