CSIRO PUBLISHING
Soil Research, 2019, 57, i–iii
https://doi.org/10.1071/SRv57n6_FO
Foreword
Céline Duwig
A
, Karin Müller
B
, Francesco Morari C, and Patrice Delmas
D
A
Université Grenoble Alpes, CNRS, IRD, Grenoble INP, IGE, F-38000 Grenoble, France. Email: celine.duwig@ird.fr
Plant & Food Research, Bisley Road, Hamilton 3214, New Zealand. Email: karin.mueller@plantandfood.co.nz
C
Department of Agronomy, Food, Natural Resources, Animals and Environment, Agripolis, University of Padova, Viale
Dell’Università 16, 35020 Legnaro, Italy. Email: francesco.morari@unipd.it
D
Department of Computer Science, The University of Auckland, Auckland, New Zealand. Email: p.delmas@auckland.ac.nz
B
Soils and their protection have been recognised of paramount
importance by the Food and Agriculture Organization (FAO) by
declaring 2015 as the International Year of Soils (Martín et al.
2017). Soils of natural and managed ecosystems deliver
several fundamental ecosystem services which, according to
the Millennium Ecosystem Assessment (2005), include
provisioning services (e.g. production of food, fibre, fuel),
regulating services (e.g. contaminant filtering, carbon
sequestration, erosion control, flood protection), cultural
services (e.g. recreation, tourism) and supporting services
(e.g. nutrient cycling processes) (Schwilch et al. 2016).
The links between soil-related ecosystem services, soil
functions and properties have recently been reviewed by
Adhikari and Hartemink (2016). Depending on the dynamic
interactions between physical, chemical and biological
properties, soils generate a multitude of soil functions, which
in turn support the delivery of ecosystem services. Among the
key soil properties and functions identified by these authors,
many of them are soil structure-dependant. Nowadays, it is
generally assumed that all processes in soils are directly or
indirectly dependant on soil structure (Martín et al. 2017).
Indeed, soil structure affects retention and availability of
water and nutrients, heat and air transport, root penetration,
and in turn, chemical and biological soil properties (Rabot et al.
2018).
In the last decade several Special Journal Issues have been
dedicated to new techniques and methods to advance the study
of soil structure, soil functions and their interactions. There is no
research field dealing with the relations between soil structure
with abiotic (e.g. water, gas, particles) or biotic (e.g. roots,
microorganisms) factors, where X-ray computed tomography
(CT) has not been widely applied in the last twenty years.
The special publication of the Soil Science Society of
America (Anderson and Hopmans 2013) ‘Soil–Water–Root
Processes: Advances in Tomography and Imaging’
emphasised the role that X-ray CT and other imaging
techniques have played during the last 20 years in the study
of soil and root interactions. In Geoderma’s Special Issue
‘Structure and function of soil and soil cover in a changing
word: characterization and scaling’ (Martín et al. 2017), authors
presented research on the parameterisation of structure being
scale-dependent and examples on how structure is related to
processes in soils. The role of different 3D high resolution
Journal compilation Ó CSIRO 2019
imaging techniques along with advances in imaging processing
that allow visualising water and transport processes in soil were
reviewed in the special section ‘Non-invasive imaging of
processes in natural porous media’ published in Vadose
Zone Journal (Li et al. 2018). The breakthrough role of
X-ray CT in the understanding of the growth and activity of
microorganisms in soils and sediments was highlighted in
the special issue ‘Elucidating microbial processes in soils
and sediments: microscale measurements and modelling’
published in Frontiers in Microbiology (Baveye et al. 2018).
This recent rich publishing activity, as also evidenced by an
analysis of papers published on the topic (Fig. 1), clearly
demonstrates the wide interest in X-ray CT applications and
the continuous and rapid advancement of imaging techniques.
In comparison to the papers published only six years ago in
Anderson and Hopmans’ (2013) Special Issue, impressive
advancements have been made in both X-ray CT technology
and image processing. This highlights the potential that these
techniques, with the exponential improvements in the
capabilities of X-ray CTs (e.g. with regard to resolution,
power, and speed) and imaging approaches, can serve as
common ground for interdisciplinary studies of the complex
nature of soils.
PROTINUS (PROviding new insighT into INteractions
between soil fUnctions and Structure) was a project funded
between 2014 and 2018 by the European Union’s Horizon 2020
research and innovation programme. It aimed to develop new
experimental, imaging and modelling approaches in order to
evaluate the impact of soil structure on soil functions.
PROTINUS assembled a multi-disciplinary team that
combined expertise in soil physics, biology and chemistry, as
well as image acquisition and analysis and numerical
modelling.
A selection of the project’s results is presented in this Special
Issue along with other related studies. The 14 papers of this
Special Issue contribute to improving current approaches of
characterising soil structure and its evolution with internal or
external factors as well as discuss the effect of soil structure on
functions associated to storage and filtering of water, mass and
gas transport, nutrients cycle and habitat for biological activity.
The scale investigated ranges from micropores to macropores,
as in these papers the main tool used to image soil structure is
X-ray CT at micron resolution.
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C. Duwig et al.
Soil Research
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Number of articles
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600
500
400
300
200
100
0
2000
2004
2008
2012
2016
Publishing year
Fig. 1. Evolution of the number of journal articles including the terms
‘X Ray CT and soil science’ from 2000 to 2018. Source: Scopus, Elsevier,
accessed 30 July 2019.
The papers are arranged in five sections: a methodological
section, followed by a section on the studies of soil structure
characterisations and three sections on the links between soil
structure and physical, chemical and biological functions.
The first two papers describe the development and
application of new methodologies related to the use of X-ray
CT in soil sciences, a novel image segmentation technique and a
new approach to visualise the distribution of particulate organic
matter (POM) in soils are introduced. Several image processing
steps are necessary to obtain parameters quantifying soil
structure from X-ray CT 3D reconstructions. The choice of
the image processing techniques will impact the resulting pore
network. In particular, the segmentation to distinguish the pores
from the solid is a crucial step (Smet et al. 2018). Azhar et al.
(2019, this issue) provide an automated image segmentation
strategy, use more robust than current state-of-the art methods.
Soil organic matter is a key component of soil structure and an
integrative indicator of land degradation. Piccoli et al. (2019,
this issue) demonstrate that, thanks to the use of contrast agents,
POM can be discriminated from the mineral fraction and its
content successfully estimated.
In the second section of this Special Issue, soil structure
evolution due to internal and external factors is characterised by
means of X-ray CT and other imaging techniques. Soil structure
is a dynamic property at different time scales and evolves with
pedogenesis, root growth and different soil management
practices. Amato et al. (2019, this issue) show that mucilage
produced by myxodiaspores during seed germination alters soil
structure and strongly binds soil. This is a transient but crucial
time of crop production when the soil is totally or partially bare
and soil stability depends on the relation between germination
mechanisms and microorganisms. At larger time scale,
Pogosyan et al. (2019a and 2019b, this issue) studied two
types of subsoil horizons: one indurated subsoil from
volcanic origin (Tepetates) and one high density horizon
from a Luvisol (fragipan). These hard layers usually prevent
root growth and water infiltration but little is known about their
genesis. The 2D and 3D quantitative studies of the pore spaces
show that pores of different sizes were formed at distinct
stages: the small homogeneously distributed pores of the
Tepetates were formed during the primary compaction, and
large crack pores appeared later, while the clay coating
infilling the cracks participated in a secondary compaction.
The pore system of the fragipan is heterochronous: the mainly
closed micropores were formed at the time of structural
collapse while fissures appeared later.
In the third section of this Special Issue, the authors
demonstrate how X-ray CT data can improve our
understanding and modelling of hydrodynamic functions.
Shiota et al. (2019, this issue) predict the drainage water
retention curve by applying the voxel percolation method
(VPM). VPM is a morphological approach under the
assumption of capillary-dominated quasi-static flow. X-ray
CT was used during a drainage experiment. The resulting
images were segmented for solid, air and water phases.
Permeability is another key soil function that is dependent
on soil structure. Ortega Ramírez et al. (2019, this issue)
compute the permeability by solving the Navier-Stokes
equation into the 3D structure of Fontainebleau sand and
virtual pack of spheres obtained at different resolutions. The
conflict between the need of good resolution, the computational
power requirement and the size of the sample increases the
difficulty inherent to direct numerical simulation in real 3D
porous structure. Müller et al. (2019a, this issue) found that
structural parameters derived by X-ray CT were significantly
related to indicators of preferential flow and that they can predict
solute transport. In soils under different land uses and
anthropogenic pressures, Yi et al. (2019) also found significant
positive influence of soil macropore properties derived by X-ray
CT on the pore water velocity or the solute dispersion coefficient.
The subtle interactions between soil structure, chemical
properties and management were investigated in the fourth
section. Indeed, agricultural management such as tillage,
irrigation, crop type or animal treading modifies soil
structure. Andosols are characterised by unique soil physical
properties such as high water retention capacity, low bulk
density and high permeability due to the presence of
amorphous compounds that can be lost by inadequate
agricultural practices (Duwig et al. 2019, this issue). Baniya
et al. (2019, this issue) and Müller et al. (2019b, this issue)
found that pore structural parameters derived from X-ray CT,
were affected by compaction and that these allowed a fair
prediction of several important mass transport parameters
such as saturated hydraulic conductivities, soil-gas diffusion
coefficients and soil-air permeabilities.
Soil structure is also affected by compaction, for example
through grazing of crops in situ. This modifies soil aeration
conditions and can lead to high emissions of nitrous oxide and
leaching of nitrate to aquifers (Thomas et al. 2019, this issue).
Soil water repellency (SWR) is another transient process
linked with soil structure through microbial activities. SWR
implications on soil properties were addressed in the last section
of this Special Issue. Some enzymes activities were strongly
correlated with the development of SWR and could help the
development of treatments to remediate SWR and improve
water infiltration and soil water storage (Simpson et al.
2019, this issue).
These results of the PROTINUS project plus the
reinforcement of international research networks through the
project set the base for future investigations of soil structure and
soil functions in a world under much climate and anthropogenic
pressure. Soils are among the key resources to overcome some
Foreword
Soil Research
of the threats humanity is facing, such as improving soil
management to ensure food security for the world’s rising
global population and increasing carbon storage in soils to
lower the threat of climate change (Schlesinger and
Amundson 2019). It also demonstrated that X-ray CT may
serve as a common ground for interdisciplinary studies in soil
soils, combining expertise in research fields only apparently far
from each other.
Conflict of interest
The authors declare no conflict of interest
Funding statement
European Union’s Horizon 2020 research and innovation
programme 645717.
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