ArticlePDF Available

Autonomous Wireless Sensor Networks in an IPM Spatial Decision Support System


Abstract and Figures

Until recently data acquisition in integrated pest management (IPM) relied on manual collection of both pest and environmental data. Autonomous wireless sensor networks (WSN) are providing a way forward by reducing the need for manual offload and maintenance; however, there is still a significant gap in pest management using WSN with most applications failing to provide a low-cost, autonomous monitoring system that can operate in remote areas. In this study, we investigate the feasibility of implementing a reliable, fully independent, low-power WSN that will provide high-resolution, near-real-time input to a spatial decision support system (SDSS), capturing the small-scale heterogeneity needed for intelligent IPM. The WSN hosts a dual-uplink taking advantage of both satellite and terrestrial communication. A set of tests were conducted to assess metrics such as signal strength, data transmission and bandwidth of the SatCom module as well as mesh configuration, energetic autonomy, point to point communication and data loss of the WSN nodes. Finally, we demonstrate the SDSS output from two vector models forced by WSN data from a field site in Belgium. We believe that this system can be a cost-effective solution for intelligent IPM in remote areas where there is no reliable terrestrial connection.
Content may be subject to copyright.
Autonomous Wireless Sensor Networks in
an IPM Spatial Decision Support System
Mina Petri´c 1,2,3,* , Jurgen Vandendriessche 4,5, Cedric Marsboom 1, Tom Matheussen 1,
Els Ducheyne 1and Abdellah Touhafi 4,5
1Avia-GIS NV, 2980 Zoersel, Belgium; (C.M.); (T.M.); (E.D.)
2Department of Physics and Astronomy, Faculty of Sciences, University of Gent, 9000 Gent, Belgium
3Department of Physics, Faculty of Sciences, University of Novi Sad, 21000 Novi Sad, Serbia
4Department of Electronics and Informatics, Vrije Universiteit Brussels, 1050 Ixelles, Belgium; (J.V.); (A.T.)
5Lumency bvba, 1020 Brussels, Belgium
This paper is an extended version of our paper published in: Petri´c, M.; Marsboom, C.; Matheussen, T.;
Ducheyne, E.; Vandendriessche, J.; Touhafi, A. Autonomous Wireless Sensor Networks in automated IPM
(CloudTech 2018), Brussels, Belgium, 26–28 November 2018.
Received: 15 April 2019; Accepted: 23 May 2019; Published: 28 May 2019
Until recently data acquisition in integrated pest management (IPM) relied on manual
collection of both pest and environmental data. Autonomous wireless sensor networks (WSN) are
providing a way forward by reducing the need for manual offload and maintenance; however, there
is still a significant gap in pest management using WSN with most applications failing to provide
a low-cost, autonomous monitoring system that can operate in remote areas. In this study, we
investigate the feasibility of implementing a reliable, fully independent, low-power WSN that will
provide high-resolution, near-real-time input to a spatial decision support system (SDSS), capturing
the small-scale heterogeneity needed for intelligent IPM. The WSN hosts a dual-uplink taking
advantage of both satellite and terrestrial communication. A set of tests were conducted to assess
metrics such as signal strength, data transmission and bandwidth of the SatCom module as well as
mesh configuration, energetic autonomy, point to point communication and data loss of the WSN
nodes. Finally, we demonstrate the SDSS output from two vector models forced by WSN data from a
field site in Belgium. We believe that this system can be a cost-effective solution for intelligent IPM in
remote areas where there is no reliable terrestrial connection.
wireless sensor networks; integrated pest management; spatial decision support system;
LoRa; satellite communication; Aedes albopictus
1. Introduciton
Pest monitoring and control is becoming an increasingly important issue worldwide, with invasive
pest species seizing the spotlight and adapting to new environments at an alarming rate. This is
supported by the impact of climate change turning previously unsuitable areas to current and future
hotspots for invasive species and emerging infectious disease. The main threat of invasive species
is their ability to vector a wide array of diseases. The World Health Organisation (WHO) estimates
that vector-borne diseases account for more than 17% of all infectious diseases, with more than
9.8 billion people at risk, 96 million reported cases, and over 700 thousand deaths annually [
Efficient local monitoring or surveillance is essential to prevent the spread and establishment of pests,
especially in ports, warehouses with imported plants, stockpiles of tires, rest areas on highways and
Computers 2019,8, 43; doi:10.3390/computers8020043
Computers 2019,8, 43 2 of 19
train stations. The European Centre for Disease Control (ECDC), the European Environment Agency
(EEA), and health/environmental protection agencies in all EU member states are responsible for the
implementation of mosquito surveillance programmes. There are still many regions in Europe without
any kind of mosquito surveillance programmed being implemented, but this is rapidly changing due
to the threat of climate change.
The role of precise in situ sensor data, as well as Earth Observation (EO), is manifold. Remote
sensed data can provide information for determining ecoclimatic zones with different levels of
environmental suitability for the pest and precise WSN data can drive intelligent dynamical population
models to target peaks in the pest population and inform control action, limiting the harmful effect on
the environment from the excessive application of pesticides.
Sensor networks are already widely used in many urban and suburban settings. This number will
only increase given the rise of “Internet of Things” (IoT). According to Gardner there are already more
connected “things” than people in the world. The number of devices in the IoT network is expected to
reach 20.4 billion by 2020 [
]. Accordingly, there have already been a number of studies to monitor and
control pests using WSN technologies. However, there is still a considerable gap in pest management
using WSN with most current applications failing to provide a low-cost, self-sufficient monitoring
system that can operate in remote areas. A lot of the existing systems rely on the availability of a power
grid and WiFi or a cellular communication network. This is not a problem in urban areas however,
pest management requires surveillance in remote areas where a local network and power supply are
not present, and the dependency on terrestrial networks is untrustworthy.
In addition to the lack of coverage, communication reliability and data acquisition and processing
delays are also a significant consideration. Until recently, data acquisition in integrated pest
management (IPM) relied on manual collection of pest and meteorological data. This is tedious
and cumbersome and incompatible with the models being developed to assist pest monitoring
mainly because of the lag created by manual collection and processing. These models rely on
NRT (near-real-time), subdaily environmental parameters to create the forcing fields necessary for
computation. Satellite communication could provide a solution to the limitations of current systems
and an uninterrupted NRT forcing for pest population dynamics forecast models.
Although local and cellular networks are widespread and commonly used, the spatial distribution
is not homogenized around the world. They are mostly concentrated around major population
hotspots. Large gaps in the spatial coverage of cellular networks do exist. This makes it hard to
conduct automatic surveying and monitoring in remote locations.
Another reason in favor of using multiple communication modules within a single WSN is
redundancy in case of weather interference. Cloud cover and precipitation can significantly affect
the availability in the SatCom link. The attenuation of the uplink and downlink signals due to rain
depend on the precipitation rate as well as the droplet size relative to the frequency of the satellite
communication band, with the degradation increasing with frequency. The principal effect behind this
is the attenuation of electromagnetic radiation passing through a liquid water medium. The highest
attenuation occurs at the Ku-band (downlink frequency 12 GHz) which corresponds to the wavelength
of 25 mm, while the lowest attenuation occurs for the C-band frequency (downlink 4 GHz) with the
wavelength of 75 mm [
]. The closer the wavelength is to the diameter of the raindrop, which averages
around 5 mm, the higher the attenuation of the incoming electromagnetic radiation. With 10/10 cloud
cover and precipitation present, the SatCom link will be unavailable. On the other hand, the terrestrial
link, while also experiencing attenuation, does so in a lesser manner with GSM frequency bands
spanning from 380–900 MHz [4].
To secure reliable data feeding into IPM spatial decision support systems we have developed the
PentaSense WSN framework, which, coupled with EO at different spatial scales feeds into numerical
models. The gateway is constructed with a dual-uplink module integrating both terrestrial and satellite
communication. This creates the possibility to implement a back-up system where both options are
Computers 2019,8, 43 3 of 19
available to increase reliability further and minimize operating costs. Moreover, embedded energy
scavenging techniques can ensure long battery life.
The aim of this research is not to replace the terrestrial communication strategy but to provide a
dual mode on the gateway to accommodate the highest degree of technological flexibility, especially
for implementations that need to be accommodating to different pest environments worldwide.
This will allow the smart traps and sensors to operate even when the terrestrial systems are or
become unavailable. Adding satellite communications on the gateway also allows for easier system
deployment. Where using local 2G/3G/4G networks requires contracts with local providers which
need to be closed in each country of operation, satellite communication allows operating everywhere
on the globe under the same contract and provider. This can be a very useful feature for prospecting
operations and pilot studies.
Hence, in the PentaSense system the satellite communication is used a second communication link
ensuring reliable, uninterrupted data transfer and redundancy for IPM applications. The dual-uplink
can provide safe, cost-effective and secure communication even in areas where existing connections are
overloaded, destroyed or not present. Moreover, this setup can provide a reliable transfer of payload
meteorological data to the remote server in NRT regardless of the deployment location of the WSN.
Impact on Integrated Pest Management
During the last decade, there was a significant shift in pest control towards integrated pest
management (IPM) approaches and practices. The implementation of many mechanistic pest
population dynamics models, as well as disease model which directly build on the previous, enables
us to apply intelligent, eco-friendly control measures before the pest achieves a significant density.
Wireless networks deployed to sense the micrometeorological variables of the environment of the
pest coupled with earth observation products such as MODIS [
] and Sentinel [
] form the basis of the
input fields driving these population and disease models.
Very high-resolution satellite images have been used to a limited extent as a means to determine
habitat of insects in general [7] and disease vectors more specifically. De Roeck et al. [8], for example,
used EO to determine the habitat of the vector of liver fluke, F. hepatica in Flanders, with a spatial
resolution of 0.5 m. Mairota et al. [
] assessed at multiple scales the required grain for pest habitat
detection. Datir et al. [
] demonstrate the application of a real-time system for the detection of the
Downy Mildew pest. Srivastav et al. [
] developed a WSN alarm system based on the noise level
generated by the pest; similarly, Srinivas [
] and Al-Manie et al. [
] look at acoustic levels for larvae,
and pests inside infected date palm trees, respectively. An overview of is given in Azfar et al. [14])
There are many IPM applications available online in the form of internet-based information
delivery systems [
]. Although most applications are in the form of static data repositories, there are
also dynamical IPM tools that use weather and climate data as input to GDD (Growing degree-day)
models [
], sampling cost calculator [
], as well as more complex phenology and pest population
dynamics models [
]. Some authors suggest that SDSS systems could quickly become an absolute
requirement for local, regional as well as international implementations of IPM surveillance and
management programs [
]. Ambient temperature has the most significant impact on mortality and
development rates for the majority of pest species; however, other abiotic factors such as precipitation,
relative humidity, soil moisture, wind speed and level of urbanization, as well as biotic parameters
such as density-dependent mortality can have an influence on the population dynamics [2022].
The potential for very high-resolution EO features to be used for measuring and monitoring
habitat quality and biodiversity is confirmed, yet important scaling issues exist and must be taken into
consideration. The computational costs involved in the choice of different computational scales for
textural high-resolution EO features are substantial as computational time increases exponentially with
increasing window size. This is especially relevant for insects where very high resolution is required.
WSNs can provide in situ, high resolution, NRT monitoring of the processes essential to the
pest life cycle in the zones outlined by EO analysis. The data collection and network design should
Computers 2019,8, 43 4 of 19
be driven by the following requirements: (a) Measurement fidelity; (b) Sampling frequency: ideally
measurements should be taken every 3 min and optimally every min; (c) Accuracy, precision and
range: preferably, the sensor accuracy should not be less than: <
C for air temperature; <
5% for
relative humidity and <
4% for precipitation. The operation range for the temperature sensor should
20 to +70
C; (d) A sustainable power supply for long-term field operation: The low power aspect
of WSNs can allow for exploring energy-efficient options that would eliminate the requirement for
a battery on the sensory nodes such as embedded energy harvesting with supercapacitors; and (e)
Harsh environment and enclosure: To ensure reliable data collection over longer periods, both the
node hardware and sensors must perform well under harsh conditions.
Basic data cleaning and aggregation algorithms need to be employed to generate forcing for all
the sites in parallel and combine on different scales. Quality Control (QC) of the incoming data must
be done in near-real time or shortly after the measurements to minimize data loss and shorten the time
to identify and fix problems.
Pest population dynamics are driven by environmental factors at the global and local scale.
The El Niño/Southern Oscillation Index (ENSO), for example, is a global phenomenon with an
impact on human infectious disease risk worldwide through droughts, flood, and other weather
extremes [2326].
On the other side of the time spectrum, locally measured rainfall/temperature with
very high temporal frequency will also drive the population dynamics more directly [
]. Capturing
the micro-meteorological conditions that are specific to pest resting sites could significantly increase
the accuracy of currently used population dynamics models as well as disease transmission models
since the processes pertaining to disease incubation rates are also temperature dependent [29].
In this paper, we examine the application of the “PentaSense” wireless network on a specific
vector, Ae. albopictus, best known as the Asian tiger mosquito. It was first introduced in Europe
around the end of the 20th century and has since spread to most of the countries on the continent.
This mosquito has vector competence for a wide range of disease such as Dengue, Yellow fever,
Chikungunya and Zika [3033].
The main environmental factors influencing the establishment of this mosquito and driving the
inter-annual population dynamics are temperature and precipitation. Climate normals and long-term
averages can be used to describe the niche regional suitability for the establishment of the vector,
however daily and sub-daily values of the meteorological variables are needed to drive the population
dynamics. Autonomous Wireless Sensor Networks (WSN) can provide precise, site-specific information
of the most important variables in remote areas and allow us to model the vector population.
The paper describes the developed WSN-SDSS framework and the results of two model
applications for the simulation of climatic suitability and micro-meteorological driven dynamics
of Ae. albopictus.
2. Materials and Methods
2.1. The PentaSense Network
The ground sensors form a WSN with a smart gateway, surrounded by modular, multi-sensor
nodes in a multi-hop mesh. The complete system is divided into three semi-independent parts, the
PentaSense WSN, the communication module and the SDSS (spatial decision support system) which
will aggregate WSN sensor and meta-data with EO on a remote server. Each multi-sensor node
communicates the collected data to the central sink node or the gateway. The gateway is equipped
with a two-way communication system integrating a satellite module and terrestrial communication.
In addition, finally, the SDSS is designed to store the data in a local database, and to analyze and
display the information in an easy to interpret way for the user through a web application. Overview
of the system architecture is shown in Figure 1.
Computers 2019,8, 43 5 of 19
The design of the communication framework considers aspects like end-to-end reliability, expected
network lifetime and existing infrastructure, etc. A power-independent WSN designs that provides
low-power, low-cost and reduced data rate wireless transmissions either in mesh networks is evaluated.
Figure 1. Overview of system architecture.
2.2. Controler Board
The PentaSense board connects up to five external sensor or communication devices with the main
controller (Figure 2). It also provides the flexibility to be AC or DC powered and can be configured
using a USB-HDI connection. The board has an integrated RF-communication module which operates
on the 866 MHz frequency. Optimized time-division multiplexing based meshed routing protocol is
implemented on the board to overcome communication distance limitations. The controller board is
built around a PIC18F46J50 microcontroller which supports a range of features that can significantly
reduce power consumption during operation such as alternate run modes, multiple idle modes,
and on-the-fly mode switching.
This can be done by using several techniques such as clocking the controller from the timer source
or the internal RC oscillator (up to 90% reduction), the control can remain operational with only the
peripherals active on the CPU core disabled.
A fully-featured USB communications module with a built-in transceiver that is compliant with
the USB Specification Revision 2.0 is incorporated with low-speed and full-speed communication.
The controller board provides ample room for application code, from 16 Kbytes to 64 Kbytes of
code space.
The Flash cells for program memory can sustain up to 10,000 erase/write cycles, while data
retention is over 20 years. It is possible to read/write the flash program memory during normal
operation. The PIC18F46J50 family also provides plenty of room for dynamic application data with up
to 3.8 Kbytes of data RAM. The board incorporates a range of serial and parallel communication
peripherals. This device also includes two independent Enhanced USARTs and two Master
Synchronous Serial Port (MSSP) modules, capable of both Serial Peripheral Interface (SPI) and I2C
(Master and Slave) modes of operation. The board provides five antilog A/D converters with a
Computers 2019,8, 43 6 of 19
sampling frequency up to 100 KS/s. The 5 A/D conversion channels are time multiplexed. The board
can operate between 2.15 V–3.6 V.
Figure 2. Basic architecture of the PentaSense WSN node.
2.3. Communication Module
2.3.1. RF Communication Module
The communication board contains a fully integrated ISM Band Sub-GHz Transceiver (MRF89XA).
The MRF89XA is a single chip, multi-channel FSK/OOK transceiver capable of operating in the
863–870 MHz license-free ISM frequency bands. The MRF89XA module is optimized for very low
power consumption and supports data rates up to 200 kbps. It incorporates a baseband modem
with data handling features that include a 64-byte FIFO, packet handling, automatic CRC generation,
and data whitening. The size and compact architecture allows for flexible integration.
The RF (radio frequency) communication parameters are made programmable and most of them
may be dynamically set. The MRF89XA uses several low-power mechanisms to reduce overall current
consumption and extend battery life. The MRF89XA complies with European (ETSI EN 300-220) and
United States (FCC Part 15.247 and 15.249) regulatory standards.
The RF communication module is equipped with a wide-band half-duplex transceiver, and
it supports proprietary sub-GHz wireless protocols and power-saving modes. The operating
voltage is 2.1–3.6 V with low current consumption typically
3 mA in receiver mode;
25 mA
at +10 dBm in transmitter mode, and 1–2
A in Sleep mode. It is operational in temperature
from 40 C to 85 C
which make it well suited for IPM deployment in harsh environments.
Furthermore, the communication module supports high data rates of up to 200 kbps and NRZ coding.
It has a wide receiver signal strength with dynamics range (70 dB from RX noise floor). The module
houses a built-in synchronizer for incoming data, and clock synchronization and recovery and 64-byte
transmit/receive FIFO with preload in standby mode
2.3.2. Satellite Communication
The Rockblock Mk2 module for satellite communication [
] was chosen to test the integration
abilities of satellite communication in the PentaSense smart gateway. Both evaluation modules are
based on the Iridium 9603(N) Short Burst Data Module which can be configured through a serial
interface by means of AT-commands, UART interface. The RockBlock 9603 module has a serial interface
over USB which allows for configuration and communication with the module. The module supports
a two-way communicaiton with global coverage. The power supply needs to be of minimum 100 mA
at 5 V DC, however, it can also run the unit directly from a 3.7 V DC LiPo/Lilon battery.
Computers 2019,8, 43 7 of 19
2.3.3. LoRa Communicaiton Module
The LoRa module can be interconnected with the communication ports (Port 1-5; Figure 2) of
the PentaSense wireless sensor node. The LoRa module is based on Microchip’s RN2483 Low-Power
Long Range LoRa Technology Transceiver module provides an easy to use, low-power solution for
long-range wireless data transmission. The RN2483 radio complies with the LoRaWAN Class A
protocol specifications. It integrates RF, a baseband controller, command Application Programming
Interface (API) processor, making it a complete long-range solution.
The communication module houses an onboard LoRaWAN protocol stack which with ASCII
command interface over a universal asynchronous receiver-transmitter (UART) and possible device
firmware upgrade (DFU) over it. The compact size of the module makes it easy to attach and house
within the same environmental shelter as the smart gateway with castellated SMT pads for PCB
mounting. This module is operational in the same range as the RF communication module making
it easy to combine, it has lower power consumption with programmable RF communication bit rate
up to 300 kbps with frequency shift keying modulation. The model has an integrated microcontroller
unit, radio transceiver with an analog front end and 14 general-purpose input/outputs for control and
status. The module is equipped with the RF analog feature able to operate on 866 MHz frequency
bands hence eliminating the need for integrating both modules for low-range point to point within the
mesh as well as long-range gateway-to-gateway communication. The TX power is adjustable up to
+14 dBm with high-efficiency power amplifiers. The range can go up to 15 km at a suburban and 5 km
in an urban area of course depending on the elevation profile.
2.4. Embedded Energy Harvesting
The PentaSense module has the ability to be powered through the USB connector. This gives the
flexibility to use any of the shelf waterproof power banks with an integrated solar cell for autonomous
use. Depending on the number of attached sensors and the expected data rate, a power bank with a
minimum capacity of 5000 mAh is used. Current power banks deliver much higher capacities and
provide as such much more reliable autonomy for the sensor nodes. A rule of thumb for the capacity
estimation is:
PowerBankCapacity = [(DCRF ·15) + (DCL ·30) + (DCSi ·PSi)] ·24 ·Daut (1)
is the duty cycle time of low power radio in daily percentage,
is the duty cycle time
of LoRa in daily percentage,
is the duty cycle time of
in daily percentage,
is the
power used by
, and
stands for the days of guaranteed autonomy (Battery requires
18 h
direct sun complete charging)
The SIMICO S3 Foldable Solar powerbank (10.000 mAh) was chosen among a set of 6 candidates,
mainly because it can support experiments with different sizes of the solar panel area. It has a capacity
of 10.000 mAh, internal batteries, four solar panels and 2 USB connections (2 ×1000 mA, 5V).
2.5. Gateway
A dual-core tablet running on Windows 10 was used as a gateway prototype for the PentaSense
system (Figure 3). It takes the role of managing the data-storage, to make the decisions regarding
the choice for the communication medium and interfaces to external communication and localization
peripherals. The tablet acts as the central sink for the WSN, and is a communication hub for the SatCom
short messages, to communicate through 3 G or GPRS, and to create a precise anchor localization
through GPS.
This architecture allows us to rapidly prototype and test the envisioned gateway functionalities.
It can also be very useful due to the availability of a display which can be used as a keyboard-less
interface for on-field configuration of the system. Moreover, it also allows for tethering with
a smartphone in case the tablet is sealed in an environmental shield or just placed and remote
Computers 2019,8, 43 8 of 19
configuration by a smartphone is necessary. The tablet also incorporates a low power SSD hard disk to
achieve long term data-retention and operate in a low power-consumption mode. Data compression
and data aggregation is applied before sending the data through payed connections.
With an external solar panel and battery, the system can operate autonomously for several weeks
or even months. This requires further optimization of the OS. To increase the autonomy of the gateway,
it is necessary for the tablet to go regularly in sleep mode or at least to turn off the display when no
user interaction is required. Putting the tablet in sleep mode might lead to specific problems regarding
the power provision of the communication peripherals. To avoid this, it is necessary to enable USB
power availability when in sleep mode and to set-up wake up timers.
To monitor the system and to provide a way to remotely upgrade the gateway, we have
investigated off the shelf tools for remote access support. In this study, we examined two tools—a
freeware tool (The Cloudberry Remote Assistant [
]) and a licensed tool (Teamviewer [
This remote access tool allows for taking over all the functionalities of the Windows-based smart
gateway. It can restart the gateway and send over files to perform a local upgrade of the gateway.
The greatest advantage of this tool is that it can be set up for unattended access. All users with the
access key can remotely access the system and no personal interaction is required. A disadvantage of
the tool is that a Windows system is required to perform the remote access. It does not support tablets
or smartphones. The TeamViewer software is a commercial tool which is used worldwide and provides
the ability to incorporate the functionalities in your own application. This means that it is not necessary
to install a separate remote access software once compiled into your own application. It is a proven tool
and is used by many companies for remote assistance. The tool is very well designed and gives remote
access to the smart gateway trough many devices. We have positively tested remote access through an
Android smartphone. Other devices like tablets are also supported. One disadvantage of the tool is
that it does not support unattended access by default. This means that once the smart gateway reboots,
a local person should send over the auto-generated access-key (password) to re-establish a connection.
During the tests, it happened that we lost control over the machine and a person had to be sent to
retrieve the key from the smart gateway. The software, however, can provide permanent access to a
remote computer (i.e., our smart gateway) through a mechanism of partner-list. This tool is not free
and requires a yearly fee per user.
Figure 3. Basic architecture of the PentaSense WSN gateway.
2.6. SDSS
The WSN and EO data are stored in a database and fed to the SDSS which is run on a remote
server. Due to the high modularity of the WSN system the SDSS can support numerical models that
generate the following outputs for different pest species and diseases: (i) Hotspot analysis and risk
maps; (ii) Population Dynamics Forecasts and Alarms; (iii) Disease risk assessment. It is envisioned as
an administrative tool for IPM applications. The backend to the SDSS uses the following technologies:
C# with ILNumerics library for in-house developed algorithms. ILNumerics can be used under a
Computers 2019,8, 43 9 of 19
commercial license. The SDSS uses SailsJS together with the Angular framework. SailsJS acts as the
backend, hosting all the API endpoints and handling the database requests. Angular acts as frontend,
loading all needed data from the API and visualizing this data in a web browser. Moreover, the Iridium
RockBlock module at the WSN sink, provides basic communication services which can be easily
activated and followed up using a generic web application.
It can integrate products such as MODIS and Sentinel. MODIS is widely used in the field of spatial
modeling and overs several very useful products. Standard derivatives as normalized difference
vegetation index (NDVI) and enhanced vegetation index (EVI) are widely accepted standards in
environmental modeling. Other derivatives such as day and night surface temperature are useful in
specific models. This data is supplemented with multi-year averages such as WorldClim version 2
data [
]. The MODIS (moderate-resolution imaging spectroradiometer) instrument is built by Santa
Barbara Remote Sensing and is installed on two satellites: Aqua and Terra. The Modis instrument
captures 36 spectral bands in 0.4–14.4
m wavelength range. Its spatial resolution varies depending on
the band: 250 m for bands 1–2, 500 m for bands 3–7 and 1000 m for bands 8–36.
The Sentinel missions are part of the Copernicus program, which is the European earth observation
mission coordinated by the European Commission together with ESA. With the recent launch of the
Sentinel-2b satellite, Copernicus has now a temporal resolution of 5 days. Sentinel 2 has three different
spatial resolution (10, 20 and 60 m) and 13 spectral bands in the visible and near infrared (VNIR) and
short-wave infra-red (SWIR).
On Figure 4the conceptual layout of the SDSS is shown. Parameters such as specific user
parameters (number of field sites, pest data etc.), the spatial scale, and type of model are set at the start
of the integration. On the other hand the control action parameter acts as a dynamic external forcing
parameter that can be supplied to the already running numerical integration.
Figure 4. Conceptual layout of the spatial decision support system.
The total cost of the hardware is estimated at
1874 for a system consisting of: One gateway with
a satellite communication module, terrestrial communication module and energy harvesting device;
Computers 2019,8, 43 10 of 19
and six PentaSense boards measuring temperature, relative humidity and pressure with an external
energy harvesting solution. Additionally, the cost of maintaining the SDSS is estimated at
180 per
user annually, making the total cost of implementation e2024.
Case Study: ASSESSING the Climatic Suitability for the Establishment of Aedes albopictus in Belgium
Two possible outputs of the SDSS models were explored. A statistical analysis of general climatic
suitability and single-point dynamical simulations for an invasive mosquito species Ae. albopictus for
Belgium and a populationd dynamics model forced by the WSN data. The data was processed in the
the R-project software environment ([38]).
(a) MCDA model simulating the climatic suitability of Aedes albopictus in Belgium:
To look at the climatic suitability for the establishment of the invasive mosquito species
Ae. albopictus
in Belgium we employed a mechanistic Multi-Criteria Decision Analysis model following
previous work of Petri´c et al. [
]. This model consists of sigma fuzzy membership functions used to
map the suitability corresponding to climatic thresholds limiting the ability of the vector to overwinter
and reproduce during the active season.
The climatic parameters (30-year averages for the reference period 1971–2000) that were selected
as input to the model are: (i) Mean annual temperature; (ii) Total annual precipitation; (iii) Mean
temperature for June, July, and August; (iv) Mean January temperature and (v) Precipitation
frequency expressed as number of days within a year with rain >1 mm. Finally, we use NTL
(night-time light) [41]
remote sensed data as a proxy for human population density and outputs
from a digital elevation model for estimating the vertical temperature gradient during the interpolation
with the co-Kriging algorithm.
The climate data were obtained from the WorldClim online database [
] with a resolution of
30 arc-seconds (1 km).
(b) WSN as input to a dynamical Ae. albopictus population model:
For this paper, we looked at the output from a pilot test of the PentaSense system in a field site in
Sint Truiden (Belgium) at the Pcfruit institute [
]. The nodes cover an area of approximately 1.4 ha.
Temperature data has been collected from September 2018 and is still in place. The system consists of 4
PentaSense nodes using Lora and RF 866 MHz point to point communication and a smart Gateway
with the RockBLock 9603 SBD Module and 3G communication Modem. The SDSS generates forcing
time-series files based on input from the Wireless Sensor Network.
The dynamic model consists of a nonlinear, coupled set of 10 prognostic ordinary differential
equations focusing on the main phases in the life cycle of the pest [
]. The model is integrated with a
daily time step using an implicit Adams numerical scheme and forced with temperature-dependent
external parameters.
Finally, we compare the WSN data that was used to force the mosquito population dynamics
model with long term averages for the current climatology (reference period 1981–2010). For this, we
used the ERA5 re-analysis data from ECMWF [
] which offers hourly time series of surface variables
on a 30 km grid. The grid point nearest to the WSN was selected.
3. Results
3.1. Testing the WSN
Several tests were performed to get the primary metrics describing the Quality of Service (QoS)
provided by the PentaSense WSN. These measurements give us statistical data that can support
different configurations of the network. Moreover, the results highlight the factors that need to be
considered when testing WSN networks within the IPM framework. A summary of the results is
shown in Table 1.
Computers 2019,8, 43 11 of 19
Table 1. Summary of test results.
Test Name Test Parameters Measured Target
Signal Strength
RockBlock signal strength; cloud cover
10/10; raining 1 3
RockBlock signal strength; cloud cover
10/10; no rain 2 3
RockBlock signal strength; cloud cover
5/10; no rain 3 3
RockBlock signal strength; cloud cover
3/10; no rain 4 3
RockBlock signal strength; cloud cover
0/10; no rain 5 3
Data Loss
Number of transmissions 100 100
Number of packets billed 100 100
Number of packets received 96 90
Bandwidth No of packets with full pay-load
(340 bytes)/min 20 >6
Coarse Grain Localization
Localization error; RockBlock signal
strength 5 <2 km -
Localization error; RockBlock signal
strength 4 <5 km -
Localization error; RockBlock signal
strength 3 <15 km -
Localization error; RockBlock signal
strength 2 <30 km -
Localization error; RockBlock signal
strength 1 >30 km -
Point to point communication
Maximum data rate; 50 m distance 48 kbps Max data
loss <2%
Maximum data rate; 40 m distance 64 kbps Max data
loss <2%
Maximum data rate; 30 m distance 128 kbps Max data
loss <2%
Maximum data rate; 20 m distance 256 kbps Max data
loss <2%
Energy autonomy Still alive signal at 0 dBm to sink every 10 s
charged at
end of test
Min 8 weeks
Mesh network configuration 15 sensor, 30 m, 48 kbps 15 15
Automated discovery Automatic discovery of 15 sensors by the
gateway <30 s <1 min
Data loss test
24 h; number of allowed retransmissions 0 <3% <1%
24 h; number of allowed retransmissions 1 <1% <1%
24 h; number of allowed retransmissions 2 <0.2% <1%
24 h; number of allowed retransmissions 3 <0.2% <1%
24 h; number of allowed retransmissions 4 <0.2% <1%
Computers 2019,8, 43 12 of 19
3.1.1. Testing the SatCom Module
Software in C# was developed to test the SatCom module so that the it could be easily configured.
The developed software allowed us to test the following parameters of the RockBlock SBD module:
(a) Signal quality with use of embedded antenna; (b) Data loss and reliability; (c) Bandwidth; (d) Use
of course grain localization by means of trilateration without use of GNSS.
Signal strength: The signal strength is examined on a 0–5 level scale, 0 meaning no connection
and 5 signifying maximum signal strength. Signal strength was 0 for cases where the module did
not have a clear view of the sky. When placed outdoors, the test demonstrated signal attenuation
as a function of cloud cover and precipitation. Signal strength varied between
1 and 5.
A reliable
connection (
3) was reached when cloud cover was less than 5/10. Concerning precipitation, the
extent of signal attenuation depends on the rate as well as on the raindrop size. The interference
during the test was significant, reducing the signal to 0.
Data Loss: Since the RockBlock SBD module does not store information for tracking the number
of lost data packages, for the purpose of this test we developed a set with sequenced, numbered
and time-stamped data packets with the maximum payload (i.e., 340 bytes). The test was carried
out on three segments of the communication chain: (i) The number of transmissions requested
by the sink; (ii) number of transmissions billed by the RockBlock data-operator; and (iii) number
of packets received at the sink. Two configuration bugs were discovered: a discrepancy in
the number of sent and number of billed packets which can be attributed to the module itself,
and another between the number of billed and the number of packets received at the sink which
is related to the signal strength. Namely, when the signal strength is below 3 some packets that
were billed were not received at the sink.
Bandwidth: The RockBlock 9603 SBD module operates with RF between 1616–1626.5 MHz.
The bandwidth depends heavily on weather conditions such as cloud cover, precipitation and
in a lesser manner temperature and relative humidity. The attenuation effect of rain depends
on the ratio of the corresponding uplink wavelength and raindrop diameter. We were able to
send up to 20 data-packets with full payload per minute without data loss under ideal signal
conditions (level 5).
Course Grain Localization: The communication module provides very basic course grain
localization without the need for an extra GPS module, reducing the overall cost of the system.
The localization precision exhibited significant variation with the radius between 2 and 30 km
depending on the strength of the SatCom signal.
3.1.2. Testing the WSN Nodes
Point to point communication: Firstly, the maximum distance between the sensor and sink was
determined as the distance at which RSSI is 0 dBm (1 mW). Indoors this value was 50 m.
Secondly, we consider data rates at different increments of the maximum distance (50 m), while
keeping the data loss rates below 2%. The rate was 48 kbps up to approximately 50 m (maximum
distance), 64 kbps up to approximately 40 m, 128 kbps up to approximately 30 m 256 kbps
(maximum data rate) up to approximately 20 m.
Energetic autonomy: The test performed consists of communicating a ‘still alive signal’ at 0 dBm
to the sink every 10 s. Full Energetic autonomy was achieved during the test (8 weeks) based
on a 10,000 mAh solar chargeable power bank. The power bank was still 75% charged at the
end of the test. The solar panels of the power bank where positioned behind a window in
North-East direction.
Mesh network configuration: An extended indoor lab test which consists of 15 sensors has been
performed. The sensors have been distributed in a three-story building, with 5 sensors on each
floor. The size of the building is approximately 30 m by 120 m. Each floor has a height of 4 m.
Computers 2019,8, 43 13 of 19
The distance between the sensors was typically 30 m, the data rate was set to 48 kbps. The test
was performed successfully with this configuration.
Automated discovery: This test was performed to evaluate the speed and ability of the sink to
discover new nodes as they are introduced. For a set of 15 newly introduced sensors, the
discovery time was bellow 30 s.
Data loss: In this test, we take a look at the number of lost data-packets due to interference,
packet collisions or other unknown influences. We found that the results depend chiefly on
the number of allowed transmissions (Table 1). The system was observed for 24 h with the
sensoring duty cycle set to 1 sample per minute with packet size of 24 bytes. The proprietary
routing protocol was based on time-division multiplexing over the network mesh.
3.2. Case Study: Aedes albopictus in Belgium
On Figure 5. The static map for the suitability of establishment of Ae. albopictus in Belgium is
shown. This static map is based on climate normals (i.e., 30-year averages) of the climate variables.
After the initial computation, it is stored in the SDSS database and called as input for defining the
eco-climatic zones with reference to which the dynamical model is called. We see that Belgium is
suitable for the establishment of Ae. albopictus with a clear difference between the densely populated
north and the south which has a smaller density of population and higher altitudes that affect the
overwintering suitability for the mosquito vector.
Figure 5.
Climatic suitability for the establishment of Ae. albopictus in Belgium based on outputs from
the MCDA model.
The output from the population dynamics simulations for Ae. albopictus forced by the WSN
measurement for one month (18 September–18 October 2019) is shown in Figure 6. This model is
forced with a daily time-step; the input from the WSN is aggregated at the end of each day and
appended to the model forcing file.
Computers 2019,8, 43 14 of 19
Figure 6.
Simulated population dynamics for Ae. albopictus based on the measured temperature from
the PentaSense WSN for the period 18 September 2018–18 October 2018.
The dynamics exhibits a negative trend which corresponds to the expected reality for the vector.
The population experiences a drop until a specific temperature and photoperiod threshold is met and
the adults die-off. Only the eggs transition into the next year.
The WSN provides accurate forcing that is specific to the pest microhabitat. Another important
aspect of having site and time specific forcing is emphasized in Figure 7where we look at the deviation
of the measured temperature value from the 30-year ensemble for the same period within the reference
period (1981–2010). We see that for this specific model run the temperature was significantly higher
than the climatology. This influences the mosquito activity and onset of autumn diapause.
Figure 7.
A comparison of the observed WSN temperature values (dark green) and the ERA5 1981–2010
climatology (box plot) for the period indicated 18 September (261 doy) to 18 October (291 doy).
Computers 2019,8, 43 15 of 19
4. Discussion
In this paper, we described our experimental PentaSense WSN network set-up in a field site in
Belgium and output generated by two models related to the climatic suitability for the establishment
and meteorological suitability driving the inter-annual dynamics of the mosquito vector Ae. albopictus.
Thus, we examined the feasibility of integrating an autonomous low-cost wireless sensor network with
a spatial decision support system meeting the specific requirement of IPM applications.
We designed, executed and analyzed a set of tests evaluating the basic Quality of Service of
the WSN. Firstly, the following metrics were considered for the SatCom module: (i) Signal Strength;
(ii) Data Loss; (iii) Bandwidth; and (iv) Course Grain Localization. Secondly, for the WSN nodes
we performed tests for the following functionalities: (i) Point-to-point communication; (ii) Energy
autonomy; (iii) Mesh network configuration; (iv) Automated node discovery; and (v) Data loss.
The results showed that the signal strength of the SatCom module was highly dependent on the
fraction of the sky obscured by clouds, and for values above 5/10, the signal strength would be low
enough to cause data loss which was observed in the number of billed and received data packets.
During the test, we discovered several configuration bugs which lead to loss of data due to the SatCom
module itself. Our best guess is that this happens when a data packet is received at the server of
the service provider, but the CRC shows a malicious receipt. The packet is billed, but not sent to the
end-application due to data corruption. This only happens under the condition that the signal strength
is below level 3. This type of data loss can be avoided by having the data sent only when the signal
strength is 3 or higher. The system performed well regarding the evaluated metrics and met the criteria
for IPM deployment.
The WSN is suitable for large-scale as well as small-scale applications. The scale of the system
will significantly depend on the pest species and type of real-world deployment. For certain mosquito
vectors small-scale monitoring with a denser sensor network is important to capture the micro-climatic
conditions of the resting habitats; while, for example, for the olive fruit fly (Bactrocera oleae) sensors
coupled with automated traps are used on larger spatial scales with a less dense network to monitor
the population across the orchards which can span from 100–500 trees for small orchards in Turkey
to 2000–5000 trees for big orchards which are typical for Spain and Australia. The system has a high
degree of modularity in terms of the spatial scale of deployment due to the global coverage of the
Iridium SBD module as well as high availability of public LoRa providers, with LoRaWAN being
the leading open global standard for secure LPWAN connectivity and wide range communication.
For small inter-node distances of up to 50 m, the nodes communicate with RF while for greater
distances the system uses LoRa communication, while the traffic load and number of nodes in our
application was small. The total network yield for standard IPM applications (up to 30 nodes per ha)
is still relatively low and will not impact data loss due to delivery or end-to-end delay.
The outputs of the suitability model for Ae. albopictus are in accordance with previously published
work [
] indicating that Belgium is suitable for the establishment of the invasive vector species.
Ae. albopictus has last been detected in 2016 [
] and previously in 2013 and 2014 [
]. The mosquito is
still not established in Belgium, however, is crossing the border from neighboring countries such as
Germany and France. The spread needs to be closely monitored to prevent the mosquito from gaining
a foothold in Belgium. Models supported by WSN data can guide surveillance and monitoring efforts
on a country level.
Although we cannot test the simulated population dynamics it exhibits a realistic trend in
which the population density decreases up to the diapausing threshold defined by critical values
for temperature and photoperiod [
]. Higher temperatures indicated in Figure 7lead to a shift of
diapause date to a later time thus prolonging the seasonal activity of the disease vector.
Climate change projections indicate that by the end of the century Belgium is expected to undergo
a significant rise in temperature, 1.7–4.9
C for winter and 2.4–6.6
C for summer. However, climate
change will also lead to a possible increase in extreme events such as heat stress and cooling degree
Computers 2019,8, 43 16 of 19
days as well as extreme values for maximum and minimum temperatures [
] making it essential
to register extreme events on a local scale with high temporal resolution to inform timely action.
The PentaSense network is currently being tested in field settings and the next step will be testing
the software for the dual-uplink as well as the robustness of system hardware in remote areas and
harsh environmental conditions. Considerations need to be taken so that the WSN is deployed in ways
that capture land use heterogeneity. Suitable biotopes for sensor placement and sensor density can be
identified using EO. Moreover, on-site tests should always be conducted to test validity and reliability.
WSN in combination with cloud services and satellite technologies have the potential to have
great impact on the way IPM is conducted worldwide. New algorithms that allow for the combination
of ground measured and modeled data at multiple scales will provide information on when and how
to conduct pest control with minimal impact on the environment.
Author Contributions:
Conceptualization, M.P., E.D. and A.T.; Data curation, M.P. and A.T.; Formal analysis, M.P.,
J.V. and A.T.; Funding acquisition, M.P., C.M., E.D. and A.T.; Investigation, M.P., J.V., C.M. and A.T.; Methodology,
M.P., C.M., E.D. and A.T.; Project administration, M.P., E.D. and A.T.; Resources, M.P., E.D. and A.T.; Software, M.P.,
J.V., T.M. and A.T.; Supervision, E.D. and A.T.; Validation, M.P. and A.T.; Visualization, M.P.; Writing—original
draft, M.P., C.M. and A.T.; Writing—review & editing, M.P., J.V., C.M., T.M., E.D. and A.T.
The work described in this paper was realized as a part of the feasibility study ‘SenZitall” co-funded by
ESA, under the Integrated Applications Program.
Conflicts of Interest: The authors declare no conflict of interest.
The following abbreviations are used in this manuscript:
API Application Programming Interface
CRC Cycle Redundancy Check
EO Earth Observations
IPM Integrated Pest Management
MCDA Multi Criteria Decision Analysis
NRT Near Real Time
NRZ Non Return To Zero
PCB Printed Circuit Board
RF Radio Frequency
SBD Short Burst Data
SMT Surface Mount Technology
SPI Serial Peripheral Inerface
USART Universal Synchronous/Asynchronous Receiver/Transmitter
WAN Wide Area Network
WSN Wireless Sensor Network
World Health Organisation. Vector Borne Disease. Available online:
fact-sheets/detail/vector-borne-diseases (accessed on 14 April 2019).
Gartner. Newsroom: Press Release. Available online:
do?id=3598917 (accessed on 14 April 2019).
Das, S.; Maitra, A.; Shukla, A.K. Rain attenuation modeling in the 10–100 GHz frequency using drop size
distributions for different climatic zones in tropical India. Prog. Electromagn. Res. 2010,25, 211–224.
4. Sharma, A.; Jain, P. Effects of rain on radio propagation in GSM. Int. J. Adv. Eng. Appl. 2010,2010, 83–86.
MODIS. NASA, Moderate Resolution Imaging Spectroradiometer. Available online: https://modis.gsfc. (accessed on 14 April 2019).
Sentinel Mission. ESA, Sentinel-2 Data Products. Available online:
missions/sentinel-2/data-products (accessed on 14 April 2019).
Computers 2019,8, 43 17 of 19
Rochlin, I.; Ninivaggi, D.V.; Hutchinson, M.L.; Farajollahi, A. Climate change and range expansion of the
Asian tiger mosquito (Aedes albopictus) in Northeastern USA: Implications for public health practitioners.
PLoS ONE 2013,8, e60874, doi:10.7282/T3JD4V1H.
De Roeck, E.; Van Coillie, F.; De Wulf, R.; Soenen, K.; Charlier, J.; Vercruysse, J.; Hantson, W.; Ducheyne, E.;
Hendrickx, G. Fine-scale mapping of vector habitats using very high resolution satellite imagery: A liver
fluke case-study. Geospat. Health 2014,8, S671–S683, doi:10.4081/gh.2014.296.
Mairota, P.; Cafarelli, B.; Labadessa, R.; Lovergine, F.; Tarantino, C.; Lucas, R.M.; Nagendra, H.;
Didham, R.K.
Very high resolution Earth observation features for monitoring plant and animal community structure across
multiple spatial scales in protected areas. Int. J. Appl. Earth Obs. Geoinf. 2015,37, 100–105.
10. Datir, S.; Wagh, S. Monitoring and detection of agriculture disease using WSN. IJCA 2014,87, 09758887.
Srivastav, N.; Chopra, G.; Jain, P.; Khatter, B. Pest Monitor and control system using WSN with special
referance to Acoustic Device. J. Entomol. Zool. Stud. 2013,3, 92–99.
Srinivas, S.; Harsha, K.; Sujatha, A.; Kumar, N.G. Eff cient Protection of Palms from RPW Larvae using
Wireless Sensor Networks. Int. J. Comput. Sci. Issues 2013,10, 192–200.
Al-Manie, M.A.; Alkanhal, M.I. Acoustic detection of the red date palm weevil. Int. J. Signal Process.
1, 1–12.
Azfar, S.; Nadeem, A.; Basit, A. Pest detection and control techniques using wireless sensor network:
A review. J. Entomol. Zool. Stud. 2015,3, 92–99.
Bajwa, W.I.; Coop, L.; Kogan, M. integrated pest management (IPM) and Internet-based information delivery
systems. Neotropical Entomol. 2003,32, 373–383.
University of Caifornia, Acriculture and Natural Resources. DD Models: Insects, Mites, Diseases, Plants,
and Beneficials. Available online: (accessed on 20 May 2019).
Uspect—Agricultural, Pest Management, and Plant Biosecurity Decision Support in the US. IPM
Pest and Plant Disease Models and Forecasting. Available online:
(accessed on 20 May 2019).
Southwest Technical Resource Center for School IPM. IPM Cost Calculator. Available online: http:
// (accessed on 20 May 2019).
University of Caifornia, Acriculture and Natural Resources. California PestCast: Disease Model Database.
Available online: (accessed on
20 May 2019).
Damos, P. Modular structure of web-based decision support systems for integrated pest management.
A review. Agron. Sustain. Dev. 2015,35, 1347–1372.
Brown, J.H. On the relationship between abundance and distribution of species. Am. Nat.
,124, 255–279.
Rousse, P.; Gourdon, F.; Roubaud, M.; Chiroleu, F.; Quilici, S. Biotic and abiotic factors affecting the flight
activity of Fopius arisanus, an egg-pupal parasitoid of fruit fly pests. Environ. Entomol. 2009,38, 896–903.
Patz, J.; Githeko, A.; McCarty, J.; Hussein, S.; Confalonieri, U.; De Wet, N. Climate change and infectious
diseases. Clim. Chang. Hum. Health Risks Responses 2003,2, 103–132.
Poveda, G.; Graham, N.E.; Epstein, P.R.; Rojas, W.; Quiñones, M.L.; Velez, I.D.; Martens, W.J. Climate and
ENSO variability associated with vector-borne diseases in Colombia. El Niño South. Oscill. Multiscale Var.
Glob. Reg. Impacts 2000,1, 183–204.
Harvell, C.; Kim, K.; Burkholder, J.; Colwell, R.; Epstein, P.R.; Grimes, D.; Hofmann, E.; Lipp, E.;
Osterhaus, A.;
Overstreet, R.M.; et al. Emerging marine diseases–climate links and anthropogenic factors.
Science 1999,285, 1505–1510.
Hales, S.; Weinstein, P.; Souares, Y.; Woodward, A. El Niño and the dynamics of vectorborne disease
transmission. Environ. Health Perspect. 1999,107, 99–102.
Abiodun, G.J.; Maharaj, R.; Witbooi, P.; Okosun, K.O. Modelling the influence of temperature and rainfall on
the population dynamics of Anopheles arabiensis. Malar. J. 2016,15, 364, doi:10.1186/s12936-016-1411-6.
Ahumada, J.A.; Laoointe, D.; Samuel, M.D. Modeling the population dynamics of Culex quinquefasciatus
(Diptera: Culicidae), along an elevational gradient in Hawaii. J. Med. Entomol. 2004,41, 1157–1170.
Paaijmans, K.P.; Imbahale, S.S.; Thomas, M.B.; Takken, W. Relevant microclimate for determining the
development rate of malaria mosquitoes and possible implications of climate change. Malar. J.
,9, 196,
Computers 2019,8, 43 18 of 19
IUCNGISD. Global Invasive Species Database. Available online:
(accessed on 14 April 2019).
31. Paupy, C.; Delatte, H.; Bagny, L.; Corbel, V.; Fontenille, D. Aedes albopictus, an arbovirus vector: From the
darkness to the light. Microbes Infect. 2009,11, 1177–1185.
Benedict, M.Q.; Levine, R.S.; Hawley, W.A.; Lounibos, L.P. Spread of the tiger: global risk of invasion by the
mosquito Aedes albopictus. Vector-Borne Zoonotic Dis. 2007,7, 76–85.
Waldock, J.; Chandra, N.L.; Lelieveld, J.; Proestos, Y.; Michael, E.; Christophides, G.; Parham, P.E. The role of
environmental variables on Aedes albopictus biology and chikungunya epidemiology. Pathog. Glob. Health
2013,107, 224–241.
Iridium. RockBLOCK Mk2. Available online:
mk2/ (accessed on 14 April 2019).
CloudBerry Lab. Free Remote Assistance Software for Windows. Available online: https://www. (accessed on 14 April 2019).
TeamViewer. Remote Support, Remote Access, Service Desk, Online Collaboration and Meetings.
Available online: (accessed on 14 April 2019).
WorldClim. Global Climate Data—Free Climate Data for Ecological Modeling and GIS. Available online: (accessed on 14 April 2019).
R Development Core Team. R: A Language and Environment for Statistical Computing; R Foundation for
Statistical Computing: Vienna, Austria, 2008; ISBN 3-900051-07-0.
Petri´c, M.; Lali´c, B.; Ducheyne, E.; Djurdjevi´c, V.; Petri ´c, D. Modelling the regional impact of climate change
on the suitability of the establishment of the Asian tiger mosquito (Aedes albopictus) in Serbia. Clim. Chang.
2017,142, 361–374, doi:10.1007/s10584-017-1946-8.
Petri´c, M.; Lali´c, B.; Pajovi´c, I.; Micev, S.; Ður ¯
devi´c, V.; Petri´c, D. Expected Changes of Montenegrin Climate,
Impact on the Establishment and Spread of the Asian Tiger Mosquito (Aedes albopictus), and Validation of
the Model and Model-Based Field Sampling. Atmosphere 2018,9, 453, doi:10.3390/atmos9110453.
NOAA. Version 4 DMSP-OLS Nighttime Lights Time Series. Available online:
dmsp/downloadV4composites.html (accessed on 14 April 2019).
Pcfruit. Het Proefcentrum Fruitteelt. Available online:
(accessed on 14 April 2019).
Petri´c, M. Modelling the Influence of Meteorological Conditions on Mosquito Vector Population Dynamics
(Diptera, Culicidae). Ph.D. Thesis, University of Gent and University of Novi Sad, Novi Sad, Serbia,
ECMWF. Copernicus Climate Change Service (C3S) (2017): ERA5: Fifth Generation of ECMWF Atmospheric
Reanalyses of the Global Climate. Copernicus Climate Change Service Climate Data Store (CDS).
Available online:!/home (accessed on 14 April 2019).
European Centre for Disease Precention and Control. Technical Report 2009: Development of Aedes
albopictus Risk Maps. Available online:
Publications/0905_TER_Development_of_Aedes_Albopictus_Risk_Maps.pdf (accessed on 14 April 2019).
Fischer, D.; Thomas, S.M.; Niemitz, F.; Reineking, B.; Beierkuhnlein, C. Projection of climatic suitability for
Aedes albopictus Skuse (Culicidae) in Europe under climate change conditions. Glob. Planet. Chang.
78, 54–64.
Caminade, C.; Medlock, J.M.; Ducheyne, E.; McIntyre, K.M.; Leach, S.; Baylis, M.; Morse, A.P. Suitability of
European climate for the Asian tiger mosquito Aedes albopictus: recent trends and future scenarios. J. R.
Soc. Interface 2012,9, 2708–2717.
Institute of Tropical Medicine, Antwerp. New Sightings of Tiger Mosquitoes in Belgium. Available online: (accessed on 14 April 2019).
Deblauwe, I.; Demeulemeester, J.; De Witte, J.; Hendy, A.; Sohier, C.; Madder, M. Increased detection of
Aedes albopictus in Belgium: no overwintering yet, but an intervention strategy is still lacking.
Parasitol. Res.
2015,114, 3469–3477.
Computers 2019,8, 43 19 of 19
Medlock, J.M.; Avenell, D.; Barrass, I.; Leach, S. Analysis of the potential for survival and seasonal activity
of Aedes albopictus (Diptera: Culicidae) in the United Kingdom. J. Vector Ecol. 2006,31, 292–305.
Meehl, G.A.; Zwiers, F.; Evans, J.; Knutson, T.; Mearns, L.; Whetton, P. Trends in extreme weather and climate
events: Issues related to modeling extremes in projections of future climate change. Bull. Am. Meteorol. Soc.
2000,81, 427–436.
Kunkel, K.E.; Pielke, R.A., Jr.; Changnon, S.A. Temporal fluctuations in weather and climate extremes that
cause economic and human health impacts: A review. Bull. Am. Meteorol. Soc. 1999,80, 1077–1098.
2019 by the authors. Licensee MDPI, Basel, Switzerland. This article is an open access
article distributed under the terms and conditions of the Creative Commons Attribution
(CC BY) license (
Full-text available
An emerging field for environmental wireless sensor networks (WSN) is entomological vector surveillance. Sensor technology can be used to shoulder ecologically friendly practices within the integrated pest management (IPM) approach. Proper surveillance and subsequent modelling of the impact that pest and disease have on human health and crop agriculture is a pressing issue in numerous segments. Complex numerical models are being developed to generate information regarding the population dynamics of vector species and the expected circulation of vector-borne disease (VBD). These models require detailed micrometeorological forcing representative of the vector habitat to generate accurate simulations. Near real-time data offload in remote areas with flexible channels of communication for complex and heterogeneous topographies is an important component in this type of application. In this chapter, the authors provide an overview of the scope and best-practice approaches in applying WSN technology to drive IPM models.
Full-text available
Mass mortalities due to disease outbreaks have recently affected major taxa in the oceans. For closely monitored groups like corals and marine mammals, reports of the frequency of epidemics and the number of new diseases have increased recently. A dramatic global increase in the severity of coral bleaching in 1997–98 is coincident with high El Niño temperatures. Such climate-mediated, physiological stresses may compromise host resistance and increase frequency of opportunistic diseases. Where documented, new diseases typically have emerged through host or range shifts of known pathogens. Both climate and human activities may have also accelerated global transport of species, bringing together pathogens and previously unexposed host populations.
Full-text available
Aedes albopictus has become established in many parts of Europe since its introduction at the end of the 20th century. It can vector a range of arboviruses, of which Chikungunya and Dengue are most significant for Europe. An analysis of the expected climate change and the related shift in Köppen zones for Montenegro and impact on the establishment of Ae. albopictus was conducted. Outputs of a mechanistic Aedes albopictus model were validated by 2245 presence/absence records collected from 237 different sites between 2001 and 2014. Finally, model-based sampling was designed and performed at 48 sites in 2015, in a previously unexplored northern part of Montenegro, and results were validated. The Eta Belgrade University (EBU)-Princeton Ocean Model (POM) regional climate model was used with the A2 emissions scenario for the 2001-2030 and 2071-2100 integration periods. The results point to a significant increase in suitability for the mosquito and a vertical shift to higher altitudes by the end of the century. The model showed excellent results with the area under the receiver operating characteristic curve (AUC) of 0.94. This study provides a tool for prioritizing surveillance efforts (model-based surveillance), especially when resources are limited. This is the first published analysis of Climate Change that incorporates observations from the national synoptic grid and the subsequent impact on Ae. albopictus in Montenegro.
Full-text available
The Asian tiger mosquito, Aedes albopictus, is one of the world’s most dangerous invasive species. It has vector competence for a wide range of arboviruses such as chikungunya, dengue, Zika and Rift Valley fever viruses. The vector originated in Asia but has recently spread to the temperate regions of Europe and North America. Further spread to the north and the east and a shift to higher altitudes could be expected as a result of climate change. This makes modelling the regional climatic suitability for the establishment of A. albopictus in naïve regions a pressing issue. The future suitability and subsequent seasonal activity of the vector were investigated using three mechanistic models, with climatic data from the Eta Belgrade University-Princeton Ocean Model regional climate model. The results showed that after a slight decrease in suitability for the first part of the century, most of Serbia would become significantly more suitable for the establishment of A. albopictus. This is due to the simulated rise in seasonal and annual temperatures by the end of the twenty-first century. This study allows for the incorporation of regional heterogeneity in vector modelling. The spatial resolution of the maps obtained from a regional analysis is much higher than that acquired by a global model, allowing for detailed risk assessment and planning of surveillance focused on the habitats where the main introduction routes and climatic suitability are coupled. This work should be applied to all countries in the region with the risk of introduction or further spread of A. albopictus.
Full-text available
Background: Malaria continues to be one of the most devastating diseases in the world, killing more humans than any other infectious disease. Malaria parasites are entirely dependent on Anopheles mosquitoes for transmission. For this reason, vector population dynamics is a crucial determinant of malaria risk. Consequently, it is important to understand the biology of malaria vector mosquitoes in the study of malaria transmission. Temperature and precipitation also play a significant role in both aquatic and adult stages of the Anopheles. Methods: In this study, a climate-based, ordinary-differential-equation model is developed to analyse how temperature and the availability of water affect mosquito population size. In the model, the influence of ambient temperature on the development and the mortality rate of Anopheles arabiensis is considered over a region in KwaZulu-Natal Province, South Africa. In particular, the model is used to examine the impact of climatic factors on the gonotrophic cycle and the dynamics of mosquito population over the study region. Results: The results fairly accurately quantify the seasonality of the population of An. arabiensis over the region and also demonstrate the influence of climatic factors on the vector population dynamics. The model simulates the population dynamics of both immature and adult An. arabiensis. The simulated larval density produces a curve which is similar to observed data obtained from another study. Conclusion: The model is efficiently developed to predict An. arabiensis population dynamics, and to assess the efficiency of various control strategies. In addition, the model framework is built to accommodate human population dynamics with the ability to predict malaria incidence in future.
Full-text available
In 2013 and 2014, routine surveillance for invasive mosquito species was implemented in Belgium at 13 potential points of entry. Following the introduction of Aedes (Stegomyia) albopictus (Skuse 1895) to Belgium via a used tyre import company (Vrasene, Province of East Flanders) in July 2013, one female and 17 larvae were collected outdoors during a period of intensive surveillance in summer and autumn 2013, but no control measures were implemented. Although climatic conditions were suitable during the winter of 2013-2014, this reproducing population did not overwinter. Lack of genetic variation, incomplete diapause adaptation and egg desiccation due to long dry periods during diapause or competition with endemic species are possible reasons. More studies on the diapause/longevity of Ae. albopictus eggs in northern temperate climatic conditions and on the competition with endemic species in western and central Europe are warranted to assess the potential for this invasive mosquito to overwinter. Furthermore, following the detection of four Ae. albopictus larvae in a shipment of lucky bamboo at the port of Antwerp in August 2014, one female, one male, 11 pupae and six larvae were collected at the destined lucky bamboo company (Lochristi, Province of East Flanders) in autumn 2014. In this case, immediate control measures were successfully implemented at the nursery. Because of increasing threats and the absence of an invasive mosquito species control policy in Belgium, the need for a permanent vector surveillance and control plan has never been so high.
Full-text available
Pakistan is an agricultural country which depends on agriculture and crops for its economic survival. WSN is an emerging technology all over the world and it is used in agriculture for monitoring different parameters. In this paper we review literature related to general agriculture monitoring, pest disease monitoring, and different pest control mechanisms. We analyze and classify pest control mechanism in technological, non-technological and integrated solutions. Then we compare the pest control mechanisms based on their effectiveness, cost and other performance parameters. Finally, we analyze the feasibility of pest control mechanisms based on the use of WSN for farmers in developing countries. Introduction Pakistan is an agricultural country and agriculture constitutes the largest sector of the economy. Majority of the population, directly or indirectly depends on this sector. It contributes about 24 percent of gross domestic product (GDP) and accounts for half of employed labor force and our agro based products is responsible for 80% of the country's foreign exchange earnings as well as supplying the raw materials needs of the other industries of the country [3]. Pakistan loses over 2.3 million cotton bales every year due to the cotton leaf curl virus (CLCV), which is considered to be the one of the top reasons for Pakistan's low cotton yield, particularly in the Punjab region. CLCV is a deadly virus that is transmitted by a small insect called white fly: a sucking pest of cotton and vegetables [1]
Sustainable pest management implies less pesticide use and replacement by safe control alternatives. This requires decision support for rational pest management. However, in practice successfully decision-making is dependent upon the availability of integrated, high quality information. Computer-aided forecasting and related decision support systems make pest control more sustainable by avoiding unwanted consequences of pesticide applications. Here I review integrated pest management for web-based decision support systems. The major points are the following: 1. Principles of integrated pest management are compatible with sustainable agriculture. 2. Pest models serve as basis of decision making because they offer means to predict the exact time of pest phenological development and initiate management actions. Most models are climate driven. 3. New hardware technology has permitted the registration of automatically recorded climatic data. This data can be combined with pest models through logical operations and forecasting algorithms to develop software’s of pest management. 4. Dynamic web interfaces can serve as decision support systems providing the user with real time pest warnings and recommendations for management actions. 5. Ontology web programing and semantic knowledge representations provides a way to classify and describe agro-data to facilitate information sharing and data exploitation over distributed systems. 6. Most available pest management data is published on static web pages and thus cannot be classified as decision support systems. Some web-based decision support systems provide user-interactive content, and real-time pest forecasts and management support. (accepted article)