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  <front>
    <journal-meta>
      <journal-title-group>
        <journal-title>SEBD</journal-title>
      </journal-title-group>
    </journal-meta>
    <article-meta>
      <title-group>
        <article-title>Fine-grained Soil Moisture Monitoring with PLUTO⋆,⋆⋆</article-title>
      </title-group>
      <contrib-group>
        <contrib contrib-type="author">
          <string-name>Matteo Francia</string-name>
          <xref ref-type="aff" rid="aff0">0</xref>
        </contrib>
        <contrib contrib-type="author">
          <string-name>Joseph Giovanelli</string-name>
          <xref ref-type="aff" rid="aff0">0</xref>
        </contrib>
        <contrib contrib-type="author">
          <string-name>Matteo Golfarelli</string-name>
          <xref ref-type="aff" rid="aff0">0</xref>
        </contrib>
        <aff id="aff0">
          <label>0</label>
          <institution>DISI - University of Bologna</institution>
          ,
          <addr-line>Via dell'Università 50, 47522 Cesena</addr-line>
          ,
          <country country="IT">Italy</country>
        </aff>
      </contrib-group>
      <pub-date>
        <year>2023</year>
      </pub-date>
      <volume>31</volume>
      <fpage>02</fpage>
      <lpage>05</lpage>
      <abstract>
        <p>Controlling soil moisture is crucial in optimizing watering and crop performance, particularly for crops with high water demands such as Kiwi. Monitoring and simulating soil behavior are two key approaches to understand soil behavior. Proximal sensors are the most reliable way to monitor soil moisture. While in the past sensor costs limited their adoption, the progressive cost reduction makes now possible to properly capture moisture dynamics in the soil volume occupied by roots. Physically-based numerical models can be used to further understand soil moisture dynamics, but solely in an of-line manner due to their time-consuming simulations. We introduce PLUTO, a cost-efective solution that, starting from sensor data, leverages both Physically-based and machine learning models to build on-line moisture profiles for long-term watering optimization. PLUTO, relies on bi/tri dimensional sensor grids that proved to largely overcome the accuracy of previous profiles obtained with traditional sensor layouts. Besides, we provide an analysis of sensor importance that takes in consideration the trade-of between accuracy, number, and position in order to suggest a smart placement.</p>
      </abstract>
      <kwd-group>
        <kwd>eol&gt;Precision Farming</kwd>
        <kwd>Smart irrigation</kwd>
        <kwd>Machine Learning</kwd>
        <kwd>Kiwi</kwd>
        <kwd>Sensor Analysis</kwd>
      </kwd-group>
    </article-meta>
  </front>
  <body>
    <sec id="sec-1">
      <title>1. Introduction</title>
      <p>
        Controlling soil moisture is a crucial factor in optimizing watering and crop performance [
        <xref ref-type="bibr" rid="ref1">1</xref>
        ].
For instance, Kiwi (Actinidia deliciosa), our case study, has high water demand [
        <xref ref-type="bibr" rid="ref2">2</xref>
        ] and farmers
tend to perform over-watering but this results into fruits with less dry mass, complications
in maintenance after harvest, and risks such as groundwater depletion and plant sufocation.
There is the need of monitoring soil moisture so that it can be kept at optimal levels, especially
in the volume occupied by tree roots. This portion of soil is particularly subject to spatial
variability for: (i) uneven root suction, (ii) limited watering-system coverage, (iii) diferences
      </p>
      <p>Dripper</p>
      <p>Watered volume
Alongtherow</p>
      <p>Soil volume</p>
      <p>Unwatered
volume
in soil composition, and (iv) exposure to atmospheric agents. The most reliable approach to
monitor soil moisture consists of exploiting proximal sensors (i.e., installed below the ground to
monitor soil moisture in the plant root zone). Typically, a single (0D) or a line of sensors (1D)
are used for cost reasons. This limit the data precision since moisture varies in the soil volume.</p>
      <p>
        Observed moisture data have been historically enhanced with the aid of Physically-based
models (i.e., numerical solutions that encode the physical laws of hydrological fluxes; e.g.,
HYDRUS [
        <xref ref-type="bibr" rid="ref3">3</xref>
        ], CRITERIA [
        <xref ref-type="bibr" rid="ref4">4</xref>
        ]). They internally build fine-grained moisture representations, but
require (i) long time series of observed moisture data to calibrate the diferent soil and plant
parameters, (ii) an expensive and resource-consuming simulation, and (iii) frequent parameter
updates. For these reasons, they have been used to typically carry out spot researches on soil
moisture dynamics in an of-line manner (e.g., [
        <xref ref-type="bibr" rid="ref5">5</xref>
        ], [
        <xref ref-type="bibr" rid="ref6">6</xref>
        ], [
        <xref ref-type="bibr" rid="ref7">7</xref>
        ], [
        <xref ref-type="bibr" rid="ref8">8</xref>
        ], [
        <xref ref-type="bibr" rid="ref9">9</xref>
        ]). Recently, Machine Learning
models (i.e., solutions that learn patterns from a large set of examples; e.g., Artificial Neural
Network [
        <xref ref-type="bibr" rid="ref10">10</xref>
        ], Support Vector Machine [
        <xref ref-type="bibr" rid="ref11">11</xref>
        ]) have been applied. They are acknowledged for
being low resource consumer (after an of-line training phase), flexible, and robust. Yet, existing
works in literature addressed solely time series forecasting (e.g., [
        <xref ref-type="bibr" rid="ref12">12</xref>
        ], [
        <xref ref-type="bibr" rid="ref13">13</xref>
        ], [
        <xref ref-type="bibr" rid="ref14">14</xref>
        ]) and of-line
soil moisture pattern studies (e.g., [
        <xref ref-type="bibr" rid="ref15">15</xref>
        ], [16]).
      </p>
      <p>To the best of our knowledge, there is no approach aimed at creating a fine-grained
multidimensional representation of soil moisture given a sensor grid. In response, we introduce
PLUTO1 [17]: a cost-efective solution that leverage both Physically-based and Machine
Learning models to build on-line moisture profiles, whose reference application is monitoring and
long-term watering optimization. This is indeed beneficial for preserving optimal soil moisture
levels and preventing water waste. We focus on the following contributions.
• The concept of 2D/3D moisture profile as a fine-grained representation of a sensor grid.
• Two alternative solutions to compute the profile, capturing linear and non-linear patterns.
• An analysis of the trade-of between the accuracy, the number, and the position of sensors
to smartly place them.
1In Greek mythology, god of wealth, linked to the prosperity of crops.</p>
      <p>(a) Actual soil moisture.</p>
      <p>(b) Raw sensor grid
(c) Soil profile
Our work is one of the outcomes of the Agro.Big.Data.Science project [18]. The project, funded
by Regione Emilia Romagna, aims at studying and implementing digital solutions to support
smart and precision farming.</p>
      <p>The remainder of this paper is organized as follows. Section 2 provides a formal introduction
to the important domain notions for this work. Section 3 illustrates the approach in detail.
Section 4 reports the tests carried out on real data collected over two years and a sensor layout
analysis for optimal placement Finally, Section 5 draws the conclusions.</p>
    </sec>
    <sec id="sec-2">
      <title>2. Domain Formulation</title>
      <p>In orchards, where a stable watering system can be built, drip irrigation is widely used as it
enables precise watering that, in turn, reduces water waste. Figure 1 shows an example of an
orchard watered through a single-pipeline dripper system. The cubes represent the soil volume
taken by the roots of each tree. Along the row of trees, a limited distance between drippers
ensures a homogeneous watered volume (in blue); while across the rows (i.e., between two lines
of trees), the soil volume remains completely unwatered (in orange).</p>
      <p>Our goal is to create a moisture profile that represents the whole soil volume.
Definition 1 (Soil volume). Given a tree, its soil volume is a parallelepiped of soil that contains
most of the tree roots. The soil volume is centered in the tree position.</p>
      <p>Definition 2 (Sensor grid). A sensor grid  = {1, ..., ||} is an -dimensional layout of ||
sensors installed in a soil volume. Each sensor  is defined by a three-dimensional displacement
(.1, .2, .3) with respect to the center of the soil volume, and by a soil moisture value ..</p>
      <p>Depending on , the grid resembles a line ( = 1), a rectangle ( = 2) or a parallelepiped
( = 3). The monitored value depends on the sensor technology, typically sensors measure
volumetric water content (i.e., the volume of liquid water per volume of soil) or the soil potential
(i.e., the energy required by tree roots to extract water from soil particles).</p>
      <p>Definition 3 (Moisture profile) . Given an -dimensional sensor grid , the moisture profile is an
-dimensional grid  = {1, ..., | |} that approximates, in each , the soil moisture measured
by .  is fine-grained with respect to  since | | &gt; ||.</p>
      <p>Building the moisture profile, based on raw sensor measurements, requires to estimate soil
moisture of the whole soil volume at a fine-grained resolution.</p>
      <p>Example 1. Given a 2D sensor grid covering an area of 0.62 (i.e., a rectangle with a width
of 1 and a height of 0.6), we employed a sensor grid with 12 sensors (i.e., || = 12) and a
moisture profile with 1000 points (i.e., | | = 1000). As a result, we obtained a moisture profile
having a granularity of 62 (i.e., 0.62/1000) while the sensor grid granularity is 5002 (i.e.,
0.62/12). For the sake of clarity, Figure 2b shows a sensor grid with || = 9 and Figure 2c shows
a moisture profile with | | = 25.</p>
    </sec>
    <sec id="sec-3">
      <title>3. PLUTO</title>
      <p>The transformation of raw sensor measurements into a fine-grained moisture profile is achieved
through a profiling function.</p>
      <p>Definition 4 (Profiling function) . Given an -dimensional sensor grid  and a moisture profile
 , a profiling function  :  →  approximates the moisture profile  starting from the grid .</p>
      <p>The role of a profiling function is approximating the soil moisture values in those positions
of the moisture profile where a sensor is not present. A profiling function is based on sensor
grid measurements and can optionally exploit further information about the behavior of the
soil. Several profiling functions can be adopted. We propose two alternative approaches that
difer in the information exploited.</p>
      <p>• Soil-feature unaware - FU: exploits the sensor measurements only. The most obvious
choice is to carry out a linear interpolation between pairs of sensor values.
• Soil-feature aware - FA: exploits the knowledge about soil hydrological dynamics to keep
into account non-linearities and to get a more accurate estimation.</p>
      <p>Sample profiles created through the two profiling functions are reported in Figure 3. It is
apparent that the FA one encodes complex non-linearities deriving from the combined efect of
the multiple factors that characterize the soil and the plant. PLUTO data processes for the two
alternative profiling functions are sketched in Figure 4. The FU function does not require to
be fitted to a specific field and only gets sensor data as input, while the FA function is trained
ofline to capture non-linear behaviors due to specific plant and soil behaviors at hand.</p>
      <p>As to the FU profiling function, we rely on the well-known -linear interpolation, where  is
the profile grid dimensionality. Although this regression approach is bounded to linear behavior
between sensor pairs, we highlight that the composition of several linear strokes approximate a
non-linear trend. For the sake of conciseness, in the following, we describe the 2-linear case.
Given a 2D sensor regular grid , this technique carries out a linear interpolation in each
dimension independently from each other. The approach consists of two phases (Figure 5). For
each point  ∈  of the moisture profile to be computed: (i) we find the four sensors  that
determine the minimum bounding rectangle enclosing  (Figure 5a), then (ii) we compute .
(Figure 5b) by interpolating along the 1 axis first. Then, exploiting the obtained points  (blue
dots), interpolation is performed along the 2 axis and the value . is finally determined. The
trilinear procedure is analogous: it just has three steps instead of two.</p>
      <p>
        As to the FA function, we rely on a machine learning model to capture non-linear soil moisture
behaviors; in particular we built an Artificial Neural Network (ANN) that learns the moisture
dynamics from a physically-based model (i.e., CRITERIA [
        <xref ref-type="bibr" rid="ref4">4</xref>
        ]). Once trained the ANN, given
the sensor measurements, eficiently computes the moisture values at the profile granularity.
This would be not possible directly using the numerical model that requires higher resources.
The learning process is sketched in Figure 4. The farmer provides the main characteristics of
the implant (e.g., soil texture, sensor layout) so that the crop simulator is set up accordingly to
reproduce the hydrological fluxes in the case at hand. Then, historical weather conditions and
watering sessions (a period of 4-month period has proved to be suficient) are fed to CRITERIA
to generate the training data for the ANN: the input layer has one neuron for each sensor to
interpolate and the output layer has as many neurons as the number of points in  . Figure 6
and Table 1 show the ANN architecture and the related hyper-parameters tuned with the aid of
a hyper-parameter tuning process implemented with HyperOpt [19]. HyperOpt exploits
stateof-the-art optimization techniques to heuristically explore search spaces of hyper-parameters.
The ANN learns the soil behavior from simulated data in an of-line phase, which is carried out
only once at the time of installation of the system.
      </p>
      <p>(a) Bounding rectangle for 
(b) Bilinear interpolation</p>
      <p>Value
# Hidden Layers 1
# Neurons per layer 100
Activation function Tanh
Normalization Z-score
# Training epochs 50
Batch size 30
Reduce learning rate factor=2, patient=10</p>
    </sec>
    <sec id="sec-4">
      <title>4. Empirical Evaluation and Layout Analysis</title>
      <p>We tested PLUTO one of the Agro.Big.Data.Science project installations [18] located in Faenza
(Emilia Romagna, Italy). This orchard is watered through a single pipeline of drippers (distance
between drippers 40cm) and Kiwifruit vines were spaced 2m along the row and 4.5m across the
rows. Soil moisture is monitored through two installations, specifically 2D and 3D sensor grids
of – respectivelly – 12 and 15 gypsum block sensors. We monitored the soil water potential,
hence the profile values are in unit of pressure (namely, in cbar).</p>
      <p>In real-world applications, the number of sensors is by far less than those we used in our
research project. Section 4.1 leverages an incremental number of sensors to compute the profile
and the remaining as ground truth to evaluate the performance. Section 4.2 conducts an analysis
of the sensor importance according to the trade-of between accuracy and position.</p>
      <sec id="sec-4-1">
        <title>4.1. Performance Evaluation</title>
        <p>Figure 7 and Figure 9 show the system performance for – respectivelly – the 2D and 3D cases,
varying the number of input sensors. In each test, the performance is calculated as the RMSE
(i.e., Root Means Square Error, the less the better) between the ground truth and the estimated
values by the profile. To better understand the advantage provided by PLUTO, we also report
the performance of profiling based on a single sensor — 0D setting — (i.e., the de facto standard)
or a column of 3 sensors at diferent depths — 1D setting.</p>
        <p>To extend the soil moisture value of the single sensor to the entire soil volume, we must
assume the soil moisture to be constant in the whole volume. Similarly, when a column of
sensors is available, we assume that soil moisture is constant at the same depth in the soil. Since
the accuracy varies based on the sensor location, we choose the single sensor position (or the
sensor line) that minimizes the RMSE as a fair comparison baseline. The same methodology was
adopted to displace the sensors used to calculate the profile with our approach. Specifically, 2D
profiles assume soil moisture to be constant along the row, while 3D profiles have no assump</p>
        <p>In both cases, the 0D setting estimations are by far less accurate than the ones obtained by
our profiling functions. The 1D settings achieve slightly better results since it captures soil
moisture at diferent soil depths, but fails in capturing longitudinal variations. The extent of
these errors is not negligible since the optimal range for soil moisture for kiwi cultivation is
[− 100; − 300) cbar [20].</p>
        <p>RMSE for FA and FU gradually decreases as the number of sensors increases. Note that the
linear profiling function can be computed only for some sensor layouts, due to the intrinsic
geometrical constraints (i.e., the profile region must be partitioned in bounding rectangles/cubes).
The ANN profiling function always outperforms the bilinear one due to its capability to better
model non-linear behaviors.</p>
      </sec>
      <sec id="sec-4-2">
        <title>4.2. Sensor Layout Analysis</title>
        <p>
          As shown in Figures 7 and 9, accuracy varies with the number of sensors. Given a regular grid
with  sensors, several layouts are possible when  &lt;  sensors are used. In particular, while
the bilinear FU function implies some geometric constraints, in the ANN-based FA one all the
160
140
120
100
E
SM80
R60
layouts are feasible. To compare diferent layout performances and suggest the smart one, we
considered the five profiles that achieve the best performances when  ∈ [
          <xref ref-type="bibr" rid="ref3 ref6">3, 6</xref>
          ] sensors are used.
Figure 8 shows the percentage of times the grid sensor appears in one of the top-performing
layouts. Noticeably, the layouts with highest performance include the sensors that convey more
information on soil moisture. In particular: (i) the sensor just under the dripper (0, − 20)
since it is the most afected by the efects of the dripper; (ii) the sensor near the surface farthest
from the dripper (90, − 20) since it records the state of the unwatered volume and is
strongly influenced by atmospheric phenomena (e.g., sun, rain); (iii) one sensor at mid-depth
(* , − 40) since it captures the soil behavior when not directly afected by watering and
atmospheric phenomena.
        </p>
      </sec>
    </sec>
    <sec id="sec-5">
      <title>5. Conclusions and Future Work</title>
      <p>We presented PLUTO [17], an original approach to compute fine-grained moisture profiles.
PLUTO relies on a grid of soil moisture sensors and it largely outperforms previous approaches
based on a single or a column of sensors. We have shown that three sensors, properly placed in
the soil, are suficient to efectively obtain the profile.</p>
      <p>We are currently turning our monitoring system into a forecasting one. We are testing ANNs
to create a solution that initially (i.e., before the deployment of the sensors) learns from a soil
simulator and then improves its accuracy by exploiting real sensor samples collected during
operations. The overall goal is to create a prescriptive analytics system that automatically
activates the watering system based on a soil moisture prediction module fed with weather
forecasts.
using artificial neural networks, arXiv preprint arXiv:1303.1868 (2013).
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[17] M. Francia, J. Giovanelli, M. Golfarelli, Multi-sensor profiling for precision soil-moisture
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[19] J. Bergstra, B. Komer, C. Eliasmith, D. Yamins, D. D. Cox, Hyperopt: a python library for
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