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Ozone gas greatly reduced the survival of carob moth larvae in stored date palm fruit
M. Jemni 1,2,*
M. Otón 3
M. Souza 4
M.H. Dhouibi 5
A. Ferchichi 6
F. Artés 3,7
1 Regional Research Center in Oasis Agriculture Degache
2 Aridlands and Oases Cropping Laboratory, the Arid Regions Institute of Medenine, Tunisia
3 Institute of Plant Biotechnology, Universidad Politécnica de Cartagena (UPCT), Campus Muralla del Mar, Cartagena, Murcia, Spain
4 University of Mato Grosso/Alta Floresta, Brazil
5 Laboratory of Entomology. National Institute of Agronomic of Tunisia
6 Rural Laboratory. National Institute of Agronomic of Tunisia
7 Postharvest and Refrigeration Group, Department of Food Engineering, UPCT, Cartagena, Murcia, Spain
Abstract - Among the vast insect pest attacks suffered by date palm, the carob moth (Ectomyelois ceratoniae) is the most destructive causing the largest damages every season. Methyl bromide is the most effective insecticide for date palm but its use will be shortly forbidden and sustainable alternatives must be found. The current work firstly evaluated the efficacy of the eco-friendly ozone gas treatment against E. ceratoniae at larvae stage on intentionally infected Deglet Nour dates. Results showed that the mortality of E. ceratoniae depended on the ozone level and the exposure time. In fact, with 12.2 mg L-1 for 80 min the carob moth mortality was ten-fold higher (82 ± 3%) than in control samples (8 ± 3%). This allows advancing in knowing the effect of ozone gas as an emergent alternative to methyl bromide on larvae of E. ceratoniae and on its possible application at commercial scale by the handling industry of fresh date palm. But, further studies are required to reach a 100% of carob moth mortality.
Keywords: Postharvest sustainable fumigant / Ectomyelois ceratoniae / Alternative to methyl bromide / Deglet Nour cv.
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Introduction
Ectomyelois ceratoniae (Lepidoptera: Pyralidae) Zeller, commonly known as carob moth or moth of pyrale due to its ubiquity, polyphagia and polychromy, has received several names such as E. ceratoniella, pryerella, oporedestella, zelleriella or phoenicis and Spectrobates ceratoniae Z. (Dhouibi 1982). The carob moth attacks fruit on the tree in many areas of the Mediterranean basin (mostly in North Africa and Middle East), Southern Russia, South West Asia, America and Western Australia (Dhouibi 1982). The moth also infests stored products, especially dried fruits, nuts, and seeds (Abo-El-Saad et al. 2011), reducing its quality and leading to important economic losses. In Tunisia the presence of E. ceratoniae has been reported everywhere from north to south (Dhouibi 1982), being the most important and destructive insect pest attacking date palm (Phoenix dactylifera) mainly Deglet Nour, the most produced cv. (Mediouni Ben-Jemâa et al. 2004). In fact, that pest causes in Tunisia up to 20 % of date palm damage during cropping season and throughout postharvest life (GIFruits 2009), while date yield losses increase up to 30% in Morocco (Bouka et al. 2001). It has been reported that in the USA E. ceratoniae infests 10–40% of the harvestable dates annually (Farrar 2000).
Methyl bromide (CH3Br) is the most widely used postharvest fumigant as quarantine treatment against E. ceratoniae and other insects of Tunisian dates at harvest time (Hassouna et al. 1994). But, due to its harmful effects on human health, as well as on the environment, the use of CH3Br is scheduled for worldwide withdrawal application in 2015, under the directive of the Montreal Protocol on ozone-depleting substances. For that reason, the search of commercial alternatives is needed. Among them, to protect plant and animal health and commodities trading (fruit, vegetables and grains) from different insects, phosphine -PH3-, sulfur dioxide -SO2-, carbon sulfate -CS2-, carbon dioxide -CO2- alone or mixed with ethylene oxide -C2H4O-, microwaving, freezing, irradiation, heat treatment, ultraviolet (UV-C) radiation, and ozone (O3) among others, have been reported (Aegerter and Folwell 2000; Bell 2000; Leesch et al. 2003; Erjaee et al. 2006; Abo-El-Saad et al. 2011; Ben-Lalli et al. 2013).
The insecticidal effect of O3 is due to a combination of its high oxidation potential and its ability to diffuse through biological cell membranes. Upon released, O3 is very efficient in destroying microorganisms and avoiding their growth by the progressive oxidation of vital cell components, it has a potential use as an insecticide mainly for food-stored products (Whangchai et al. 2006; Abo-El-Saad et al. 2011; Niakousari et al. 2010). The O3 can be generated on-site, being able to extend the shelf-life of many intact and minimally processed fruit and vegetables, while leaving no residues since it decomposes to O2 quickly (Restaino et al. 1995; Parish et al. 2003; Guzel-Seydim et al. 2004; Artés et al. 2007). That degradation constitutes both a challenge for practical application and a benefit for the environment (Hansen et al. 2013). It has a Generally Recognized as Safe status as a food-processing aid agent for the treatment, storage and processing of foods, approved for use in direct contact with them under Good Manufacturing Practices (FDA 2001; Suslow 2004; Artés et al. 2007). Consequently, the O3 could be used in post-harvest Integrated Pest Management programs. In that way, in a preliminary study we found that dipping for 2 min in ozonated (0.6 ppm O3) water at 15ºC induced a E. ceratoniae mortality in naturally infected Deglet Nour dates of about 15% compared to about 26% in control fruits after 30 days at 20ºC (Jemni et al. 2014).
The aim of this work was to evaluate the effect of O3 gas at different concentrations and different exposure times on the survival of E. ceratoniae at larvae stage in intentionally infested Deglet Nour dates. To the best of our knowledge, this is the first report about the use of O3 gas to control E. ceratoniae on date palm.
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Material and methods
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Origin of dates and carob moth
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Dates of Deglet Nour cv. were selected because it is the most produced date palm cv. in Tunisia. The bunches of dates were hand harvested by professional pickers at the end of October at fully mature (‘Tamar’ stage) from a commercial farm located in the Oasis of the Governorate of Kebili (South of Tunisia). The bunches were placed on the ground to avoid crushing and the abscission of dates. Each bunch was then cut into spikelets and about 20 kg were placed in polystyrene boxes and transported around 500 km by car at ambient temperature to the Laboratory of Entomology of the National Institute of Agronomic of Tunisia. Dates were manually detached from the spikelets and carefully inspected, being only sound dates intentionally infested by one carob moth at larvae stage (Stage 5). About 15 kg of infested dates were then placed in ventilated polystyrene box and transported then by plane to Madrid (Spain), and finally by car around 400 km to the Pilot Plant of the Technical University of Cartagena. Total transport duration was about 7 days.
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Ozone generation
An ozonated air-flow was obtained from an industrial O3 generator producing 0.6 mg s−1 (AMBICON, Murcia, Spain). The O3 concentrations were monitored with a sensor (EcoSensors, Inc., A-21ZX model, Santa Fe, NM, USA) that was sited inside a hermetically sealed glass jar (Artés-Hernandez et al., 2003). Twenty carob moth infested dates were placed into each glass jar of 1000 mL, which were exposed to a continuous O3 enriched-air flow as described in Table 1. One glass jar was considered as a replicate, and for each experiment three replicates were used.
Table 1. Central composite design arrangement and results of percentage of carob moth mortality. Data are means (n = 60) ± SD |
|||
Trial n° |
Factors |
Y= % carob moth mortality |
|
Z1 (ppm) |
Z2 (min) |
|
|
1 |
1 |
30 |
23.34±2.8 |
2 |
5 |
30 |
31.67±2.6 |
3 |
1 |
60 |
28.34±2.8 |
4 |
5 |
60 |
45±4.5 |
5 |
3 |
45 |
30±3.76 |
6 |
0.57 |
45 |
20±5 |
7 |
5.43 |
45 |
33.34±3.6 |
8 |
3 |
26.775 |
25±5 |
9 |
3 |
63.225 |
35±4.7 |
All treated samples were then incubated at 28°C and 75% RH in air for 9 days. As control, untreated samples were used. The carob moth mortality, expressed in percentage, was calculated by the equation (1).
The carob moth mortality = (1- Nd/Ns) × 100 (%) (1)
Where Nd was the number of carob moth dead after incubation, and Ns was the total number of carob moth (Ns = 20).
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Experimental design
An orthogonal central composite design (CCD) for two factors was performed in order to determine the optimal conditions of moth mortality. The variables investigated were the O3 flow concentration and the exposure time to O3. Each variable at five coded levels (indicated as -1.215, -1, 0, 1, +1.215 as shown in Table 2) was designed as experimental runs using the Analysis Tool Pack ‘linear Regression’ in Excel 2007. The real values of the independent variable (Z) were coded according to equation (2).
Table 2 Experimental domain and distribution of variables used for the evaluation of the carob moth mortality
|
||||||||
Factors |
Symbols |
|
Level* |
|||||
Coded |
Uncoded |
|
-1,215 |
-1 |
0 |
+1 |
+1,215 |
|
[O3] ppm |
X1 |
Z1 |
|
0.57 |
1 |
3 |
5 |
5.43 |
Time (min) |
X2 |
Z2 |
|
26.775 |
30 |
45 |
60 |
63.225 |
*X1= (Z1 - 3)/2, X2= (Z2 - 45)/15
Xi = (Zi - Zi° ) / δZi (2)
Where Zi is the real value of the independent variable; Zi° is the central value; Xi is the coded value of the independent variable given by the experimental matrix. Z and X values are shown in Table (2).
The experimental response was measured as the percentage of moth mortality, which was estimated taking into account the influence of the experimental factors. A full quadratic model containing 6 coefficients was used to describe the responses observed and to fit the equation (3).
Y moth mortality = a0 + a1 × X1 + a2 × X2 + a12 × X1 × X2 + a11 × X1 × X1 + a22 × X2 × X2 (3)
Where a0 is constant, a1 and a2 are linear coefficients of O3 flow (X1) and time of exposition to O3 gas (X2), a12 was the cross product coefficients and a11 and a22 were the quadratic coefficients. The attained fit of second order equation was checked by the coefficient of determination R2. The analysis of variance and the estimation of response surface by multiple linear regressions were performed using the Analysis Tool Pack ‘Linear Regression’ in Excel 2007.
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Physicochemical parameters and sensory evaluation
Physical and chemical quality of dates were evaluated by analyzing firmness (N), pH, titratable acidity (TA), expressed as g of citric acid on kg_1 fresh weight, moisture (g kg_1 fw), water activity (aw), and color, based on CIELab* scale.
Measurement of mentioned quality parameters was accomplished as previously described by Jemni et al. (2014). Analyses were performed on dates treated with the optimum concentration of ozone and on a control sample without treatment.
Visual appearance, color, texture, flavor and overall quality were evaluated based on a five-point hedonic scale (1: extremely poor, 2: poor, 3: acceptable and limit of usability, 4: good and 5: excellent). These sensory attributes were evaluated by a trained panel (6 members ranging between 25 and 65 years) over a representative sample coming from dates treated by O3 and control dates.
All parameters were determined on three samples. Average of these samples determinations is presented. Statistical analysis was performed with Info Stat (version 1). Analysis of variance (ANOVA) and LSD test were applied in order to evaluate the influence of ozone treatment. A least significant difference (LSD) multiple range test at 5% probability level was used to determine significant differences between means.
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Results
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Predictive response model
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The matrix of the effects, which shows the tests and the responses of composite design of experiments, is given in Table 1. A carob moth mortality for control sample of 8 ± 3% was found.
The Analysis Tool Pak ‘Linear Regression’ provides statistical regression and analysis of variance (P= 0.04). The coefficient of determination R2 was 0.95, being close to 1, corresponding to a model of good quality. The coefficients values were calculated and tested for their significance. The P values are commonly used as a tool to check the significance of each coefficient. The model was represented by equation (4).
Y moth mortality = 28.15 + 5.93 × X1 + 4.38 × X2 + 2.08 × X1 × X2 + 2.44 × X2 × X2 (4)
As expected, it was found that the O3 concentration (X1) (P=0.0116) and the duration of the treatment (X2) (P=0.0264) were the most important factors (a1 = 5.93; a2 = 4.38) on carob moth mortality, while the interaction between O3 concentration and time (X1× X2) (P = 0.023)and the interaction only with time (X2 × X2) (P=0.027) were also relevant factors (a12 = 2.08 and a22 = 2.44). However, the interaction with O3 concentration only (X1 × X1) was not significant (P = 0.926).
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Trace of the response surface
The response was a hyperbolic parabolic surface which is designated in a more imaged by ‘horse saddle’ (Fig. 1). The response surfaces of the regression equations were obtained by using the Analysis Tool Pak ‘Linear Regression’. The region where the response changed little despite significant variations in the factors was located around a stationary point which the coordinates were found by differentiation.
Figure 1. Isoresponse curves showing the zone of stability of carob moth mortality. |
The solver provided an optimum dose of 12.2 mg L-1 for 80 min. The theoretical response optimized by the solver (99.995% mortality) and the target responses (100% mortality) does not show a significant difference.
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Validation of the optimum
Before recommending these results for commercial application, it was necessary to perform several new experiments for validation. In this way, the application of a continuous flow of 12.2 mg L-1 for 80 min on 20 dates infested by carob moth, replicated three times, gave a moth mortality of 82 ± 3 %.
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Physicochemical parameters and sensory evaluation
As shown by table 3, the treatment by ozone did not affect the physicochemical parameters of dates. In fact, they maintained the pH, acidity, moisture, firmness and aw. But, there is a decrease in values of color parameters (L*, Chroma and Hue°) as compared with the control. This later could be explained by browning reaction caused by O3.
Table 3 Effect of ozone on skin color parameters, pH, acidity (g citric acid/100g FW), firmness (Newton), moisture (%) and aw of Deglet Nour date treated by a continuous flow of 12.2 mg L-1 of ozone for 80 min.
|
||
|
Control |
O3 |
Color L* |
32.07±2.4 a |
30.54±2.8 b |
Chroma |
20.04±2.72 a |
17.97±4.6 b |
Hue° |
62.3±4.8 a |
60.92±7.6 b |
Acidity |
0.113±0.107 a |
0.117±0.001 a |
pH |
5.53±0.33 a |
5.51±0.27 a |
Moisture |
20.29±0.001 a |
21.27±0.82 a |
Firmness |
6.001±0.80 a |
5.58±0.54 a |
aw |
0.64±0.003 a |
0.63±0.011 a |
Data are means (n = 3) ± SD. Means followed by different letters in the same line are significantly different (p ≤ 0.05) according to LSD test. |
In addition, overall quality, texture and flavor were maintained after treatment by a continuous flow of 12.2 mg L-1 of ozone for 80 min. The color was appreciated by tasters in spite of the brown color (Figure 2).
Figure 2 Changes in flavor, texture, color and overall quality of Deglet Nour date treated by a continuous flow of 12.2 mg L-1 of ozone for 80 min. Data are means (n = 3) ± SD. |
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Discussion
The current study showed that O3 greatly disturbs the survival of E. ceratoniae larvae. In control dates a low natural carob moth mortality of 8 ± 3% was found while the rise in O3 concentration in the air flow and in the exposure time increased mortality. This could be explained by the O3 effect on lowering the respiration rate of insects (Baoqian et al. 2009) as well as by the fact that O3 acts as a toxic which can cause oxidative damage on tissues even at low concentrations (Liu et al. 2007). According to our results both the O3 concentration and the exposure time were very important factors influencing the E. ceratoniae mortality rate.
The achievement of 100% mortality derived from the theoretical responses optimized by the solver, E. ceratoniae requires an O3 concentration of 12.2 mg L-1for 80 min. However, the application of this result in experimental gave a moth mortality of 82 ± 3%. Abo-El-Saad et al. (2011) have proved that 2 mg L-1 O3 for 12 h was effective against the different developmental stages of Ephestia cautella reaching near 90% of adults’ mortality, being larvae less sensitive than adults, where mortality was about 30%. Erjaee et al. (2006) showed that an exposure of Kabkab dates to 50 g O3/day for 30 min at 20ºC killed almost 90% of the adults and larvae of P. interpunctella. More recently, Niakousari et al. (2010) have proved that exposing samples to higher than 2000 mg L-1 O3 for 120 min resulted in complete mortality of larvae and adults of Indian meal moth P. interpunctella in Kabkab dates. However, the mortality obtained in wheat for T. castaneum and P. interpunctella under a continuous O3 flow of 13.9 mg L-1 for 120 min as higher than in the experiments presented here (Isikber and Oztekin 2009). This could be explained by the different species of insects and by the concentration and contact time between O3 and the insect.
The physicochemical and sensorial qualities of dates treated by a continuous flow of 12.2 mg L-1 of ozone for 80 min were maintained and the values reached for each parameter agree with those found by Jemni et al. (2014), El Arem et al. (2011), Besbes et al. (2009) and Achour et al. (2003).
As in fact 100% of mortality was not achieved in the current work, complementary experimental studies, must be conducted. It should be also studied the combination of O3 gas with other techniques, like high CO2, within the frame of the hurdle technology, as early showed by Leesch et al. (2003).
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Conclusion
As main conclusion, the O3 gas greatly lowered the survival of carob moth larvae in Deglet Nour date palm fruit during commercial storage. The O3 gas showed a positive effect on E. ceratoniae mortality despite the presence of pulp dates as a border isolating the direct action of O3 on the moth. In fact, with 12.2 mg L-1 for 80 min the carob moth larvae mortality was about ten-fold higher than in control samples. Further studies should be conducted to optimize these preliminary results, to examine the O3 gas effects on E. ceratoniae at different stages of growth, and on its application at commercial scale. The current results provide encouragement in finding an emergent alternative to CH3Br useful for the industry of fresh date palm around the world.
Acknowledgments
The authors are grateful to Tunisian Ministry of Higher Education and Scientific Research for a predoctoral grant to M. Jemni. Thanks are also due to Laboratory of Entomology of National Institute of Agronomic of Tunisia, and to Institute of Plant Biotechnology of the Technical University of Cartagena for providing some facilities.
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