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Available online at www.sciencedirect.com ScienceDirect Procedia Technology 8 ( 2013 ) 580 586 6th International Conference on Information and Communication Technologies in Agriculture, Food and Environment (HAICTA 2013) Stochastic modeling and simulation of olive fruit fly outbreaks Spyros Voulgaris a, *, Michalis Stefanidakis a, Andreas Floros b, Markos Avlonitis a a Department of Informatics, Ionian University, Tsirigoti Square 7, Corfu 49100, Greece b Department of Audio & Visual Arts, Ionian University, Tsirigoti Square 7, Corfu 49100, Greece Abstract Lately lot of work has been done in the area of modeling insect population dynamics based on the emergency of new information technologies. In this paper we propose a real-time online alert information system for estimating the population evolution of the olive fruit fly. The proposed system simulates the evolution of the biological cycle of olive fruit fly as well as its activity in real field using mobile platforms (smartphones, tablets) for the distributed collection of data from traps and local climate and topological data thus predicting timely olive fruit fly outbreaks. Simulation results are depicted validating the robustness of the proposed information system and revealing the importance of appropriate population control measures in the right time and place. 2013 The Authors. Published by by Elsevier Elsevier Ltd. B.V. Open access under CC BY-NC-ND license. Selection and peer-review under under responsibility of The of Hellenic HAICTA Association for Information and Communication Technologies in Agriculture Food and Environment (HAICTA) Keywords: Olive fruit fly; stochastic models; population dynamics; simulation 1. Introduction The insect Bactrocera oleae commonly known as olive fruit fly or dacus, is the most serious threat of the olive and is widespread in all the oil producing countries of the Mediterranean causing enormous damage every year. For example, in Greece this insect is known since antiquity and the damage it can cause if not appropriate control measures are taken, can reach very high levels, up to 80% of total production. The damage caused by dacus can be summarized to the early fall of the olive fruits and therefore product loss prior to harvest that constitutes the most * Corresponding author. Tel.: +30-2661-087-753; fax: +30-2661-087-766. E-mail address: svoul@ionio.gr 2212-0173 2013 The Authors. Published by Elsevier Ltd. Open access under CC BY-NC-ND license. Selection and peer-review under responsibility of The Hellenic Association for Information and Communication Technologies in Agriculture Food and Environment (HAICTA) doi: 10.1016/j.protcy.2013.11.083

Spyros Voulgaris et al. / Procedia Technology 8 ( 2013 ) 580 586 581 important form of loss, and quantitative and qualitative degradation caused by the consumption of an amount of flesh from the olive fruit during its development. [1,2]. During its biological cycle the olive fruit fly goes through the following stages: egg, larva, pupa and perfect insect. In most regions of Greece, 3-4 generations appear per year. To address the problem of population control of olive fruit fly the method most widely used is chemical control namely the spraying of the olive grove with pesticides. Cover spraying aims at killing the egg and larva stage of the insect and can be performed even to a single tree but has the disadvantage of killing also a wide variety of useful organisms. Bait spraying aims at preventing mature females from laying eggs to the young olive fruits. In order for bait spraying to be effective it must be applied to a wider area and that s why they are often planned and carried out by local authorities. Generally bait spraying is considered as the most effective method [3,4]. For bait spraying timely and diligent application of the first spray is decisive for the whole olive crop period as it coincides with breeding of the first generation of the insect. Generally, the effectiveness of sprays depends largely on the correct identification of application time and space. Timing of the spraying solely on the basis of traps findings is often precarious, as the traps catch only a fraction of the population (its efficiency being subjected to seasonal effects) and does not take into account other parameters such as the weather conditions and the olive grove topography. A method of estimating the optimal time of spraying will benefit greatly both the producers and the environment as it would result at better control of the dacus infection, increased production, cost reduction from fewer but more effective spraying, protection of the environment from reduced used of chemicals and finally better product quality. To this end, a robust modeling of population dynamics is needed in order to address the complexity emerged in real field scenarios and more over in real time applications where the problem of robust (biological, climate and topographical) data about the specific olive grove must also be addressed. While complex models tend to have limited usage because of the lack of flexibility, more simple models were shown to be inefficient in predicting the population evolution in non-stationary population dynamics [5]. In the current paper a robust modeling of the evolution of olive fruit fly population is proposed based on the well known day-degree model where the complexity emerged in real field is addressed through appropriate estimation of the stochastic variation of the corresponding dynamic parameters. 2. Methodology The aim of the present work is to bring together new tools and developments in physics and computer science with new aspects in applied entomology. This interdisciplinary attempt lies in the intuition that nature complexity has the same behavior in different physical systems and in particular to those phenomena where interactions between species and up scaling procedures in order to obtain global behavior from features of insect individuals, are present. Our work elaborates on well known studies on applied entomology in population insect dynamics [6, 7]. As a milestone of the present work the selection and estimation of the corresponding mean and variance values of the key dynamic parameters as well as environmental parameters was based on real field data that were available from past years for the island of Corfu in Western Greece. More specifically, the population density and its variance were determined by pooling data from MacPhail traps from the database of the Agriculture Directorate Corfu, for the years 1991-2002, in the western Corfu (St. George area). Initially, the space (corresponding to a real olive grove of 7400kmx9000km total area) was simulated by a 2D grid where each unit cell corresponds to a 100m2 area. As a result the total grove is assumed that is covered by a grid of 74x90 MacPhail traps which monitors the dacus population. In each simulation run the values of the corresponding traps are filled using stochastic tools that statistically reproduce robust values to each trap [8]. Moreover, the population was divided into two categories: the immobile (egg, larva, pupa) and the mobile (perfect insect both mature and immature) population. For the immobile population the modeling of the biological cycle of the olive fruit fly is based on the day-degree model applied for each distinct stage: egg, larva and pupa. For the mobile population, and in order to achieve a robust modeling in real field situations the random movement of the population was studied since the dispersion of population may causes both acceleration of population growth and shift of the high stable population equilibrium to even higher values thus producing population outbreak [9]. The need to find food and olive fruit susceptible to egg deposition makes the mature insects to fly long distances. Olive fruit fly has the ability to spread over long distances, which, depending on climatic conditions, the terrain and

582 Spyros Voulgaris et al. / Procedia Technology 8 ( 2013 ) 580 586 the availability of olives, can reach 10km, but under normal environmental conditions migration is small. Local conditions of Corfu, from measurements made during June-July, found that in areas poor in olive fruits, the average distance traveled by individuals flies was more than 400m on the first week. On the contrary in olive groves with a fruit rate above 30%, the spread distance of olive flies was determined much shorter, about 180m respectively [10]. The above analysis was used in order to estimate the smallest time unit in the simulation code: is the time that a single insect needs in order to diffuse from one unit cell of the 2D grid to another. This value was estimated to be approximately 4 hours. Finally, the statistical processing of the data from the database of the Agriculture Directorate Corfu, for the years 1991-2002, were used in order to extract in real field conditions the mortality rate of the population due to the applied chemical sprays (for the next time after application) versus present population and the time of application. Our main finding shows that for the first 5 days after the spraying the mortality is up to approximately 50 % of the initial population while for the next 5 days the mortality is mostly a function of the season of the spraying application and goes up to approximately 20%. The total of the above described dynamic parameters were used as an input to the simulation code developed in order to model the evolution of the complete biological cycle of olive fruit fly (in the immobile and mobile stage) as well as its activity thus resulting to a robust population evolution in real time and in real filed conditions. The complete application platform is custom-built using open source software tools and languages. The core simulator is written in the C language for maximum speed and is in effect a discrete event simulator: it cycle-steps through all possible states (i.e. of aging, reproduction, drifting and reduction due to pesticides) for each olive fruit fly contained in the event list of insects kept during the simulation. Input files are being assembled before each simulation by helper scripts written in the Python language. A final script in Python processes also the output log of the core simulator in order to construct the log of events used by the final presentation application which was created in visual C++ environment. 3. Simulation Results The simulation code was tested based on the data accumulated during the implementation of the co-financed research project Modeling self-organization dynamics and suppression of dacus population in real Ecosystem of Saint George Municipality in Corfu in the years 2006 to 2008. Inside the olive grove a network McPhail traps was established and harvesting of the captured specimens took place every five days by specialized personnel. The simulation code produces a cell grid as shown in Fig 1. Black cells represent olive grove area, while white cells are places with low olive trees density (shoreline, settlements, cropland) which cannot sustain a measurable number of insect individuals, above a certain threshold. Fig. 1 also shows traps location as small white dots Fig. 1. Cell grid with traps location

Spyros Voulgaris et al. / Procedia Technology 8 ( 2013 ) 580 586 583 From the traps reading input we initialized the grid using interpolation techniques and the results are illustrated in Fig. 2. In each cell there is assigned a number which represents the population density of olive fruit fly in the specific cell. Non-valid cells are assigned number zero (0), but zero can also be assigned to valid cells when our simulation model estimates no olive fly presence. Fig. 2. Olive fruit fly population initialization The value of the simulator becomes apparent when different spraying scenarios are loaded to it. For every scenario it is recorded the date that the spraying will be applied, the affected area and the mortality rate of the female mature insects. We run the simulation code for two different scenarios.

584 Spyros Voulgaris et al. / Procedia Technology 8 ( 2013 ) 580 586 Fig. 3. Bad case scenario In the first case we assumed that 3 distinct sprayings are applied in the total of the olive grove according to traditional practices of local producers: most of the time it depends on weather conditions and availability of workers and materials. The results are shown in Fig. 3. It can be seen that the adaptation of random dates for the application of sprayings may result to a huge loss of the production even though a significant amount of chemical is used.

Spyros Voulgaris et al. / Procedia Technology 8 ( 2013 ) 580 586 585 Fig. 4. Good case scenario In the second scenario the olive grove is sprayed at an early stage and in selected dates, the selection being according to the optimal biological and environmental conditions of the specific stage of the biological cycle of the olive fruit fly. It can be seen that the same spraying scenario may lead to a significant reduction of the olive fruit fly infection at the end of the simulated period (Fig. 4) 4. Conclusions and Further Work In this work we investigated a new mathematical model for the simulation of the population evolution of the olive fruit fly in order to estimate the appropriate time for the application of bait spraying to olive groves. The developed software has proved its robustness and demonstrated its value in estimating the evolution of the dacus population. Utilisation of web based applications and location-aware systems can be proved very useful in the agricultural sector [11]. In our proposed system the simulation software will be integrated with an online server to which data will be uploaded from mobile devices through a user-friendly web interface. In order to achieve interconnection between platforms data will be transferred in a form that can be processed by software agents. The Extensible Markup Language (XML) is a general-purpose markup language whose primary purpose is to facilitate the sharing of data across different information systems and especially across the World Wide Web. The simulation code was designed to receive data in an appropriate XML format.

586 Spyros Voulgaris et al. / Procedia Technology 8 ( 2013 ) 580 586 References [1] Neuenschwander P, Michelakis S. Infestation of Dacus oleae (Gmel.)(Diptera, Tephritidae) at harvest time and its influence on yield and quality of olive oil in Crete. Journal of Applied Entomology 1978; 86:420-433. [2] Rice R. Bionomics of the Olive Fruit Fly Bactrocera (Dacus) olea, UC Plant Protection, 2000; 10(3). [3] Haniotakis GE. Olive pest control: present status and prospects. Integrated Protection of Olive Crops. IOBC Bulletin. 2005; 28(9):1-9. [4] Manousis T., Moore NF. Control of Dacus oleae, a major pest of olives, International Journal of Tropical Insect Science 1987; 8(1): 1-9 [5] Sharov AA. Modeling insect dynamics. In: E. Korpilahti, H. Mukkela, and T. Salonen (eds.) Caring for the forest: research in a changing world. Congress Report, Vol. II., IUFRO XX World Congress, 6-12 August 1995, Tampere, Finland, 1996. pp. 293-303.. [6] Ludwig D, Jones D, Holling C. Qualitative analysis of insect outbreak systems: the spruce budworm and forest, The Journal of Animal Ecology 1978; 47: 315-332. [7] Comins HN, Fletcher BS. Simulation of Fruit Fly Population Dynamics, with Particular Reference to the Olive Fruit Fly, dacus oleae, Ecol. Modell. 1988; 40: 213-231. [8] Avlonitis M, Anagnostou K, Vlamos P. On a probabilistic Method for exact spatial interpolation on sampling data: Application to olive fruit fly population data, International Advanced Workshop on Information and Communication Technologies for Sustainable Agro-Production and Environment (AWICTSAE), 2008. [9] Avlonitis M, Tragoudaras D, Stefanidakis M, Papavlasopoulos C. Stochastic Processes and Insect Outbreak Systems: Application to Olive Fruit Fly, on Energy, Environment, Ecosystems and Sustainable Development (EEESD'07), Agios Nikolaos, Crete, Greece, July, 2007. [10] Fletcher BS, Kapatos E. Dispersal of the Olive Fly, Dacus Oleae, during the Summer Period on Corfu, Ent. Exp. & appl., 1981; (29): 1-8. [11] Pontikakos C, Tsiligiridis TA, Drougka M. Location-aware system for olive fruit fly spray control, Computers and Electronics in Agriculture 2010; (70):355-368.