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Engenharia Agrícola

versão impressa ISSN 0100-6916versão On-line ISSN 1809-4430

Eng. Agríc. vol.37 no.3 Jaboticabal mai./jun. 2017

http://dx.doi.org/10.1590/1809-4430-eng.agric.v37n3p493-501/2017 

Scientific Papers

Agricultural Machinery Management

SPRAY DRIFT AND PEST CONTROL FROM AERIAL APPLICATIONS ON SOYBEANS

João P. A. R. da Cunha1  * 

Robson R. M. Barizon2 

Vera L. Ferracini2 

Marcia R. Assalin2 

Ulisses R. Antuniassi3 

1Universidade Federal de Uberlândia/ Uberlândia - MG, Brasil

2Embrapa Meio Ambiente/ Jaguariúna - SP, Brasil

3Universidade Estadual Paulista/ Botucatu - SP, Brasil

ABSTRACT

Pesticide drift is an issue in modern farming, mainly for crops under constant spraying as soybeans. This study aimed at assessing drift and pest control for aerial applications in soybean crops. Hydraulic nozzles and rotary atomizers, regulated to a wide spectrum of droplet sizes, sprayed thiamethoxam plus lambda-cyhalothrin using an agricultural aircraft Ipanema 202A at volume rate of 20 L ha−1. Treatments consisted of testing two devices: a rotary cage atomizer (Micronair AU 5000) with blade angles of 65° for larger droplets, and with angle of 55° for smaller ones; and a set of adjustable nozzles (Stol model) with deflector angle of 90° for smaller droplets, and with angle of 30° for larger ones. Drift was evaluated through quantification of active ingredient, by means of liquid chromatography, on nylon strings set 20, 40, 80, 160 and 320 m downwind from the applied area. Control efficiency was measured by counting caterpillars and stinkbugs found five days after spray. Rotary atomizers produced lesser drift compared to adjustable nozzles at the designed setting. Furthermore, drift can be reduced through a suitable regulation of the devices, keeping an effective pest control.

KEY WORDS: agricultural aviation; crop protection; exodrift; glycine max

INTRODUCTION

Chemical control of insects in soybeans (Glycine max L. Merrill) is a very common farming practice, mainly against caterpillars and stinkbugs. If no performed, major losses of yield are expected (AITA et al., 2015). In this sense, most attention is given to which chemical to be used rather than to the way it is applied (BUENO et al., 2011).

For the operation to succeed, a proper spraying should be mastered, ensuring product reach to the target efficiently, lowering losses and environmental contamination. Part of the applied product can be lost, especially if application techniques are being wrongly used, constituting one of the largest challenges to be overcome in modern agriculture (NUYTTENS et al., 2011; ZHAO et al., 2014).

This issue can be observed in aerial application, which is a reality in great part of grain producing areas for Brazil. Such technique has been increasing a lot lately, however, little scientific information is found regarding its effectiveness, primarily in comparison to ground boom sprayers (CUNHA et al., 2014). For ANTUNIASSI et al. (2011), the main devices for droplet generation in aircrafts are rotary atomizers and hydraulic nozzles. They provide different droplet spectra, which in turn promotes different patterns of deposition and drift.

In some countries, particularly in Europe, one of the solutions to reduce drift has been to set safety zones (buffer zones), determined from drift simulations associated to toxicological studies. These areas are vegetation strips deprived from pesticide spraying, to prevent contamination of particular sensitive areas as watercourses and inhabitable regions (ALVES et al., 2014).

Notwithstanding, the length of this lane is variable and depends on spray conditions (DE SCHAMPHELEIRE et al., 2007). Therefore, studies measuring the horizontal distance a drop can travel under several operational conditions are required to state the proper extent of these buffer zones, increasing both control efficiency and environmental safety.

Despite the environmental risk, few studies have been evaluating the drift in aerial application, especially in Brazilian conditions. Thus, this research aimed at evaluating drift and chemical control from aerial application of insecticides on soybeans, comparing rotary atomizers and adjustable hydraulic nozzles set to provide various droplet sizes.

MATERIAL AND METHODS

The research was carried out in a commercial grain producing area (2014-2015 season) in Monte Alegre de Minas, Minas Gerais state, in Brazil (18° 52' S latitude and 48° 52' W longitude).

Soybean seeds, of P98Y70 RR Pioneer late-cycle cultivar, were sown at spacing of 0.5 m between rows with 10 plants per meter. The experiment consisted of four treatments as shown in Table 1, plus four replications. These treatments were composed of two application devices sprayed by aircraft, assessing pesticide drift and efficiency to control caterpillars and stinkbugs. In both devices, it was performed two scenarios, one accounting for the worst conditions in terms of drift risk (small droplets) and another for drift reduction (large droplets).

TABLE 1 Description of the experimental treatments. 

Treatment Application device Settings Adjustment target
1 Rotary atomizer Blades at 55° Smaller size droplets
2 Rotary atomizer Blades at 65° Larger size droplets
3 Hydraulic nozzle Deflector at 90° Smaller size droplets
4 Hydraulic nozzle Deflector at 30° Larger size droplets

Sprays were carried out at R5.3 (beginning seed) when leaf area index was of 2.05, which was measured by the average of leaf areas sampled at four points of 1 m2.

All sprays were performed through an aircraft Ipanema EMB 202A, which was equipped with DGPS system, operating at 177 km h−1 (110 mph), flying three meters above the canopy, 16 m swath width and 20 L ha−1 application volume rate.

In atomizer treatments, six rotary cage atomizers (Micronair® AU 5000) were set with blades angled at 65°, for larger droplets, and at 55°, for smaller ones. The system pressure was at 193 kPa. In the another treatments, 54 hydraulic adjustable nozzles (Stol® model) were set with deflector at 90°, for smaller diameters, and at 30°, for larger ones, according to each treatment, and orifice size D6. In this case, pressure was set at 138 kPa.

According to the manufacturer of Micronair AU5000, blades at the angles of 65° and 55° promote a fine droplet spectrum, with volume median diameters (VMDs) of 203 and 142 μm, respectively, as classified by ASABE (ASABE, 2009). On the other hand, the manufacturer provide no information of droplet sizes for the adjustable nozzles, so the field conditions (flow rate and air speed) was simulated through a wind tunnel (NEMPA, FCA/UNESP, Botucatu-SP, Brazil) testing, measuring the droplet size by means of an droplet analyzer, in real time, based on the analysis of high resolution images. For that, it was used VisiSize D30 equipment (Oxford Lasers Imaging Division, England). Therefore, with deflector positioned at 90° and 30°, the set of nozzles generated a fine droplet spectrum with VMDs of 156 and 194 μm, respectively.

Experimental plots were 250 m long and 128 m wide. The aircraft passed over the target area eight times within a 16 m swath width to ensure a proper overlapping, with crosswind towards the line of application.

Spraying solution was composed of an insecticide combination of thiamethoxam (141 g L−1) and lambda cyhalothrin (106 g L−1) - Engeo Pleno®, at a dose of 200 mL ha−1, plus vegetable oil (Veget' oil® – fatty acid esters – 930 g L−1), at a dose of 300 mL ha−1.

For drift evaluation, collectors were previously set; these devices were made of PVC structures with a 2-mm nylon strings extended for 2 m vertically. These collectors were placed at 20, 40, 80, 160 and 320 m downwind from application area, counted from the borderline of each plot, making four replications for each. They were all set so that each monofilament was promptly above crop canopy.

Therefore, drift was assessed by quantification of the amount of thiamethoxam active ingredient on strings analyzed by means of liquid chromatography. To this end, nylon strands were carefully gathered shortly after application, to avoid cross-contamination, and placed into plastic bags under no light, being subsequently sent for analysis in the Laboratory of Pesticide Residues, which belongs to the Embrapa Environment, located in the city of Jaguariúna-SP, Brazil.

The samples were then cut into pieces of nearly 0.5 cm using pliers; then, a 5 g sample was weighed in a 125 mL Erlenmeyer flask. Next, 10 mL methanol was added and stirred for 48 h using a shaking table at 65 rpm and at room temperature. An aliquot of 1 mL was pipetted and filtered directly into a filtering unit (PVDF - Hydrophilic, 0.22 μm). Separations were made through a high-performance liquid chromatography (Shimadzu, Japan), consisting of a pumping system (LC 10 AT VP), auto-sampler (SIL 120 A), column oven (CTO 10A) and detection by UV-VIS (SPD 10 AV vp) at a wavelength of 254 nm. It was used a 5-μ C18 column (250 × 4.6 mm), at 0.6 mL min−1 flow rate, gradient elution mode, water-acetonitrile as mobile phase, starting at 10% acetonitrile, which was increased linearly up to 40%, during 20 minutes, keeping it for a minute, thus totaling a 30 minute run. Injection volume was of 20 μL. The thiamethoxam retention time was 20.4 minutes. Quantitation testing was performed using an analytical curve of six different concentrations (from 0.0025 to 0.2500 μg mL−1).

Once the amount of active ingredient per collector area was taken, drift index was estimated as function of thiamethoxam volume sprayed per area (28.2 g ha−1).

Drift index=βdep×10000m2ha1βV (1)

In which,

  • Drift index – relative drift index (dimensionless);

  • βdep – deposited drift (μg cm−2), and

  • βv - dose (g ha−1).

Treatment control efficiency against caterpillars (Anticarsia gemmatalis and Pseudoplusia includens) and stinkbugs (Euschistus heros, Nezara viridula and Scaptocoris castanea) was evaluated in two times, before and five days after spraying. To do so, five random sampling points were selected within each plot (6,400 m2), from where individuals were collected with the aid of a beat cloth (1.0 × 0.5 m) and counted. From the number of collected insects, control efficiency could be calculated using the Abbott's formula (ABBOTT, 1925).

During sprayings, environmental conditions were monitored as temperature, air relative humidity, wind speed and direction by means of a fully automatic weather station.

Data were compared by the confidence intervals for differences between means, at confidence level of 90% (90% CI), as described by ANTUNIASSI et al. (2011).

As already performed by HOFFMANN & KIRK (2005), field data were compared to simulations from a drift prediction software - AgDrift® (Spray Drift Task Force Spray Software, version 2.1.1), for each treatment (Table 1). This computer program takes account of climate conditions and has a specific module of drift simulation for aircraft spraying (TESKE et al., 2002), with an extensive database. However, it should be highlighted that Ipanema aircraft models were not assessed, especially regarding the winglet. Moreover, the software keeps a database of the AU5000 atomizer, but not of the hydraulic nozzles of Stol brand. Thereby, it was selected an adjustable nozzle with great similarity: CP-03 (CP Products, Texas, USA).

The correlation between observed and predicted values was made by the Pearson's method, at 0.05 significance level. Regression lines of each treatment were compared to 1-1 lines. The F-test, at 0.05 significance level, was used to test the hypothesis of intercept linear values and slope coefficient being equal to 0 and 1, respectively. For that, it was used the R software (version 2.9.2).

RESULTS AND DISCUSSION

During the applications, temperature, relative humidity and wind speed raised from 23.9 to 25.3°C, from 74 to 81% and from 5.8 to 7.3 km h−1, respectively. In brief, these variations whilst performing were low. Notwithstanding, this information is important since, among all factors interfering with pesticide drifting, environmental and weather conditions (temperature, air humidity and wind speed) are the most impacting (ARVIDSSON, 2011; HILZ & VERMEER, 2013; GIL et al., 2014).

Figure 1 displays a graphic of drift index up to 320 m far from target area. Based on this, it is noteworthy that treatments were difference, mainly within the shortest distances. Nozzles adjusted for small droplets (deflector at 90°) generated the largest drift values, reaching a relative drift of 0.728 at 20 m away, being followed by deflector at 30° (0.314). Therefore, a simple exchange of deflector angle from 90 to 30° would reduce drift, decreasing risks in 57%. Still, atomizers achieved lower values of drift compared to hydraulic nozzles, without differing from one to another, and showing mean drift index of 0.062 (91.5% reduction with regards to the worst case).

FIGURE 1 Drift curves for aerial application of thiamethoxam using rotary atomizer with blades at 55° and 65°, and hydraulic nozzles with deflector at 90° and 30°. Vertical bars stand for the confidence interval (90%). 

In summary, it was possible to infer that atomizers are most interesting tools to reduce drift when matched to adjustable nozzles. In a similar study, HEWITT et al. (1994) simulated aerial spraying by a wind tunnel and observed atomizers had a uniform droplet spectrum, decreasing thus the amount of very fine droplets, more likely to drifting.

In this sense, HOFFMANN & KIRK (2005) demonstrated that two different spray nozzles classified as medium droplets, had varying drift behaviors. Adjustable nozzles, placed 50 m apart from target, had drift values 3.2 times larger than other nozzles as discs and cores. Overall, it confirms the point of a particular constructive design for each spray system on drift behavior.

Drift comparative assessments between atomizers and hydraulic nozzles are quite uncommon in literature. Notwithstanding, a few studies have suggested atomizers to have a better performance relative to the nozzles (CALDWELL, 2006). This author noted that rotary atomizers promote lower drift, although the VMD (213 μm) was slightly lower than those using hydraulic nozzles (283 μm). The same research also highlights that other characteristics such as nozzles and atomizers arrangement along the aircraft spray boom, can also interfere with the drift results besides droplet spectrum.

The largest drift rates were observed at sampling points quite near the crop, decreasing as it moved away from the treated area. Drift curves with this profile had already been found by other authors, such as HOFFMANN & KIRK (2005) and ANTUNIASSI et al. (2014).

When evaluating the distances of 40 and 80 m, drift showed a similar behavior, in which nozzles with deflector at 90° reached the largest values (0.355), followed by those with deflector at 30° (0.143), reducing at 59.7%, just by angle adjustment. Whereas atomizers achieved a value of 0.036, being 89.9% lower than the first case. Once again, angle adjustment of blades had no effect on results.

From 160 m downwind, the differences between treatments tended to decrease with distance. For this reason, it was detailed that region of drift curve (Figure 2). In addition, again at 160 m, it was observed the highest drift index for nozzles set at 90° (0.098), followed by those at 30° (0.038), showing a reduction of 61.2%, while atomizers had no difference among the blade angles, reaching an index of 0.007 (92.9 % reduction).

FIGURE 2 Detailed drift curves for aerial application of thiamethoxam using rotary atomizer with blades at 55° and 65°, and hydraulic nozzles with deflector at 90° and 30°. Vertical bars stand for the confidence interval (90%). 

When considering the longest distance (320 m), the settings of the nozzles had no effect on drift. MOKEBA et al. (1998) stated that when droplets stop accelerating (i.e., when they travel the same speed as the surrounding air), their dispersal becomes controlled by random turbulence effects or air currents. Applications with atomizers promoted less drift (0.009) whether compared to adjustable nozzles (0.044), i.e. an average reduction of 79.6%. Nonetheless, in this study, it was not made an extensive investigation of drift reduction techniques under different operating conditions. Even though it was possible to observe that drift can be reduced just by executing a few settings, future investigations are necessary to evaluate the arrangements of nozzles along sprayer boom, as well as the use of new drop atomizers and adjuvants to minimize losses by drift.

Figure 1 have shown the drift curves designed with data gathered in field. By regression analysis, it must be pointed out that the equation of the power type had good fit to the data, although the R2 for treatments with nozzles was lower than with atomizers. This outcome might have been related to the difference between the observed and estimated values for the distance of 20 m.

Regarding pest control efficiency (Figure 3), a lack of difference among treatments for both caterpillar and stinkbugs was observed. These results just reinforce the fact that using treatments that reduce losses by drift should be clearly chosen due to their technical feasibility, particularly those with atomizers. Considering all treatments, the numbers of insects per square meter, found five days after applications, were of 0.2 caterpillars and 0.4 stinkbugs. Prior to sprayings, it was found an average number of 3.0 caterpillars and 4.8 stinkbugs per square meter, therefore, control efficiency was of 93.3% and 91.7%, respectively, which led to conclude that such insecticide has high efficiency (>90%).

FIGURE 3 Numbers of caterpillars and stinkbugs five days after aerial application of thiamethoxam using rotary atomizer with blades at 55° and 65°, and hydraulic nozzles with deflector at 90° and 30°. Vertical bars stand for the confidence interval (90%). 

Drift values estimated by the AgDrift model were compared to those obtained experimentally, and all treatments showed a significant correlation between observed and simulated values (Pearson's correlation at p < 0.05). This correlation denotes that the model satisfactory simulated drift decay trend as function of distance.

To check if the model presented any bias for curve adjustments, both observed and simulated values were plotted onto a linearized graph (Figure 4). The closer the predicted values get to the 1-1 line, the better the model fit is. For rotary atomizers at 55°, simulated values were overestimated, once they were placed below the 1-1 line. It might have occurred because the aircraft winglet was not taken into consideration, which reduces the drift values. Likewise, HOFFMANN & KIRK (2005) had also found conflicting results when comparing observed and simulated values. However, these authors claimed no explanation for such outcome. On the other hand, simulated values for hydraulic nozzle at 30° and 90° proved to have been underestimated, with all points positioned above the 1-1 line. Perhaps this may have occurred because the software has no specific database for this nozzle model. Droplet spectrum variations for each nozzle may lead to different drift value.

FIGURE 4 Thiamethoxam drift values by the use of rotary atomizer with blades at 55° and 65°, and hydraulic nozzles with deflector at 90° and 30°, both from field evaluations and simulated by AgDrift model. 

When using atomizer at 65°, simulation was overestimated for low drift values and underestimated for large ones, i.e. the drift model overestimated drift at long distances and underestimated it for short ones. To confirm that trend lines adjusted for each treatment, in Figure 4, differ from the 1-1 line, observed and simulated linearized data underwent regression analysis, and the resulting equation was compared by hypothesis testing with the 1-1 line equation (intercept = zero and slope coefficient = 1). The equations of all treatments differed significantly (F-test, p < 0.05) from the one obtained for the 1-1 line, showing that the results generated by the AgDrift model did not satisfactorily express the experimental data.

Despite these differences, this software is sensitive to differentiate treatments, which in addition to the good fit of the drift curve as function of distance denote its potential to assess risks of drift from aerial application. In this regard, a database expansion, especially regarding regional data, could enhance its simulations.

CONCLUSIONS

Rotary atomizers showed the lowest levels of drift with high efficiency to control caterpillars and stinkbugs in soybeans, whether compared to the hydraulic adjustable nozzles.

It is possible to reduce drift in aerial applications by making proper adjustments. In this sense, further studies are required to broaden the number techniques to be used for drift reduction.

Computational simulation, by means of AgDrift software, showed sensitivity to estimate drift under different operating conditions, however, simulated values differed materially from those observed in field, so its database must be broadened to include diverse local conditions.

ACKNOWLEDGEMENTS

To Empresa Brasileira de Pesquisa Agropecuária (Embrapa), for financial support; to Algar Farming and Sindag for the support in the field evaluations; and to Ricardo Almeida Antônio Pazianotto for the support in data analysis.

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Received: October 10, 2016; Accepted: October 27, 2016

*Corresponding author. Universidade Federal de Uberlândia/ Uberlândia - MG, Brasil. E-mail: jpcunha@ufu.br

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