Pesticides Research No. 116 2008 of fungicide application in winter wheat

2 Materials and methods

2.1 Field experiments

Field experiments were carried out in winter wheat at four sites in Denmark with high spatial variation in soil and terrain; two sites in each of the years 2005 (Schackenborg and Nissumgaard) and 2006 (Nissumgaard and Dybvad). The site at Schackenborg is located close to the village Møgeltønder and west of the town Tønder in southern Jutland on a sandy soil overlaying clayey deposits from the marshes. The site at Nissumgård is located close to the village Gjesing between Skanderborg and Odder in eastern Jutland on moraine deposits varying in soil type from sandy to sandy loam. The site at Dybvad is also located in eastern Jutland on moraine deposits varying in soil type from loamy sand to sandy loam.

All locations were chosen to be relatively inhomogeneous fields with respect to soil type, and at Nissumgård and Dybvad also with variable topography, in order to favour different responses to nitrogen and fungicide treatments.

Each experiment was conducted in a two-factorial design with fungicide dose and N strategy (Table 1). The fungicide treatments consisted of increasing doses of Opus (125 g L-1 epoxiconazol) applied at GS 39. The N strategies consisted of three different rates of mineral fertiliser N applied in a split treatment and a normal rate of N applied in a single treatment. In all split treatments 50 kg N ha-1 was applied in early April. The remaining N and the full rate of the single N treatment were applied at stem elongation (late April).

Table 1. Factors and treatments in the experiment.

Factor Treatment
1. Fungicide 1. No fungicide control
  2. 0.2 L ha-1 of Opus applied at GS 39
  3. 0.4 L ha-1 of Opus applied at GS 39
  4. 0.8 L ha-1 of Opus applied at GS 39
2. N-strategy 1. 160 kg N ha-1 (50 + 110 kg N ha-1)
  2. 80 kg N ha-1 (50 + 30 kg N ha-1)
  3. 240 kg N ha-1 (50+190 kg N ha-1)
  4. 160 kg N ha-1 (single application)

The experimental factors were laid out in a randomised split-plot design with N-strategy as whole-plot factor and fungicide dose as sub-plot factor. These blocks were repeated 10 times across the field in an attempt to cover most of the soil variation between replicate blocks, giving a total of 160 plots in each experiment. Net plot sizes were 27.6 m² at Nissumgård and 30 m² at Schackenborg in 2005, and 16 m² at Nissumgård and 17.7 m² at Dybvad in 2006.

The crop management details are outlined in Table 2. The previous crop was winter wheat at both sites in 2005 and winter oilseed rape at both sites in 2006. The wheat was sown in mid September in both years. The site at Nissumgård in 2005 was sprayed with manganesesulphate in April. However, despite of this, manganese deficiency could be observed in some of the plots in May.

There were three plots at Schackenborg in 2005 with errors in N fertiliser application. In about a third of plots 2108 and 2208 too little fertiliser had been applied, and plot 2811 had received too much fertiliser.

Table 2. Crop management at the two experimental sites in 2005 and 2006.

2005    
  Nissumgård Schackenborg
Previous crop winter wheat winter wheat
Variety Deben Grommit
Sowing 21-09 18-09
Harvest 01-09 18-08
N fertiliser 11-04 (1st rate) 06-04 (1st rate)
  26-04 (2nd rate) 26-04 (2nd rate)
Fungicide 08-06 (Opus) 30-05 (Opus)
Herbicide 28-10 (9 g ha-1 Lexus 50 WG) 22-04 (100g ha-1 Hussar)
  28-10 (1.5 L ha-1 Boxer EC)  
  30-04 (100 g ha-1 Hussar)  
  30-04 (0.04 L ha-1 DFF)  
  18-05 (12.5 g ha-1 Monitor)  
Insecticide   18-08 (0.1 kg ha-1 Pirimor)
Micronutrient 30-04 (2 kg ha-1 MnSO4)  
     
2006    
  Nissumgård Dybvad
Previous crop winter oilseed rape winter oilseed rape
Variety Deben Deben
Sowing 13-09 15-09
Harvest 30-08 29-08
N fertiliser 19-04 (1st rate) 19-04 (1st rate)
  05-05 (2nd rate) 05-05 (2nd rate)
Fungicide 06-06 (Opus) 02-06 (Opus)
Herbicide 06-10 (1 L ha-1 Stomp) 12-10 (1.25 L ha-1 Boxer EC)
  06-10 (0.025 L ha-1 DFF) 12-10 (0.4 L ha-1 Stomp)
  06-10 (0.15 L ha-1 Boxer EC) 12-10 (0.03 L ha-1 DFF)
  10-05 (18 g ha-1 Monitor) 12-10 (0.1 L ha-1 Oxitril CM)
Insecticide 24-10 (0.05 L ha-1 Karate EW) 20-08 (0.1 L ha-1 Cyperb)
Micronutrient 24-10 (2 kg ha-1 MnSO4) 20-10 (2 kg ha-1 MnSO4)
  10-05 (2.5 kg ha-1 MnSO4)  

The fungicide treatments including the tracer treatment were applied using an experimental plot sprayer equipped with a 2.5 m wide boom. The spray boom was equipped with conventional hydraulic flat fan nozzles with a mutual distance of 50 cm. The nozzle used was a Hardi S 4110-14 flat fan nozzle delivering 0.7 l min-1 corresponding to 230 l ha-1 at a driving speed of 3.6 km h-1.

There was a spraying error at Dybvad in 2006, where plot 4312 did not get any fungicide application.

2.2 Measurements of soil and topography

Measurements of soil texture, water content, topography etc. were made with three sensors:

  • MobilTDR (time domain reflectometry) instrument developed at Research Centre Foulum (Thomsen et al., 2005; Thomsen and Schelde, 2006). The TDR instrument is mounted on farm tractor. The MobilTDR instrument was used for making precise measurements of water content and electrical conductivity of the top 50 cm of the soil. Early season measurements of water content is closely related to the water holding capacity of the topsoil and hence the yield potential. In combination, measurements of water content and electrical conductivity are closely related to the sum of the clay and silt fractions of a given soil type. The MobilTDR instrument is only available as a single prototype. A maximum of 15-30 ha can be mapped in a single day. These measurements were included for comparison with EM38 measurements and generally to provide data of reference quality.
  • EM38 instrument mounted on a low sledge made from non-metallic materials (plastics) (Greve et al., 2002; Korsaeth, 2006). The instrument is pulled by a light ATV vehicle. The EM38 instrument is used for measuring soil electrical conductivity of the topsoil. The measuring depth varies with especially the clay and water content of the soil. The measurements are related to relative rather than absolute differences in soil texture. The commercially available EM38 instrument is widely used today and large areas can be mapped in a single day.
  • RTK (GPS) instrument. The RTK instrument is used for manual measurements of the exact position and elevation of plot corners. The data is used in the extrapolation of mobile measurements made outside plots and in the calculation of plot orientation.

Both mobile instruments (MobilTDR and EM38) were equipped with GPS (global positioning satellite) receivers for geo-referencing measurements. The mobile measurements related especially to soil texture were included in order to map differences in growth conditions for the individual plots. The mobile measurements were made outside the research plots in order to avoid disturbing the wheat crop. Consequently interpolation is needed in order to extend measurements inside the plots.

Additionally samples of the topsoil (0-20 cm) were taken across each of the fields for comparison with the sensor measurements. Ten samples were taken at each site and analysed for soil texture.

2.3 Yield measurements

The plots were harvested using a plot combiner. Crude grain yield was determined immediately after combining by weighing the amount of grain harvested in each plot. Samples were taken for subsequent analyses. The first step of the analysis was separation of grain and impurities, resulting in an estimate of percentage of impurities. The pure grain samples were analysed for content of water, crude protein and starch and for specific weight (100 litre weight) using NIT (Buchmann et al., 2001).

Based on content of impurities and water the grain yields were transformed to dry matter grain yields, which were used in subsequent analyses. Only yield was analysed further.

Due to errors at harvest, two plots at Nissumgård and one plot at Schackenborg were lost in 2005, and consequently any yield related value for these plots was set to missing in the subsequent analyses. At Nissumgård yields from 21 plots in 2006 were discarded due to errors in marking the location of the field plots. There were 6 missing yield observations at Dybvad in 2006. This number of missing data should be compared to the total of 160 plots at each site.

2.4 Disease assessments

Disease assessments were carried out 4 times in the trials with focus on Septoria tritici (septoria leaf blotch) and Blumeria graminis (powdery mildew). Cultivars susceptible to Septoria tritici were chosen to increase the possibilities of investigating the impact on this disease.

  • GS 32-33; Assessments were carried on whole plots with the 4 different N strategies. The disease severity was assessed as percentage of green area of the canopy with visible symptoms of the diseases.
  • GS 37-39; Severity was assessed in all plots. The disease severity was assessed as percentage of green area of the canopy with visible symptoms of the diseases.
  • GS 65; approximately 3-4 weeks after fungicide application. All plots were assessed. Severity of individual diseases was assessed on individual leaf levels (2nd leaf and flag leaf).
  • GS 75 approximately 30-40 days after application. All plots were assessed. Severity of individual diseases was assessed on individual leaf levels (2nd leaf and flag leaf).

Apart from plant pathogenic spots, physiological spots developed significantly in the cultivar Grommit grown at Schackenborg in 2005. These spots are cultivar specific as well as being influenced by various stress factors in the crop. The physiological spots complicated the assessment of septoria leaf blotch at GS 39 and 65 as the different symptoms can be difficult to separate. In 2006 only Sepotoria blotch developed significantly in the trials. In the report Septoria leaf blotch will generally just be called Septoria.

2.5 Sensor measurements of plants

Measurements of canopy structure (leaf area index (LAI), leaf mean tip angle (MTA) and height) and N-status were all made during two major campaigns (growth stages BBCH_32 and BBCH_39) using four instruments:

  • LAI-2000 canopy analyser from LI-COR Biosciences was used for measuring LAI and MTA (Stroppiana et al., 2006). A limited number of destructive samples were collected and analysed in the laboratory with respect to leaf area in order to check the sensor measurements. Both the total crop area index (CAI) including both green and senescent canopy material and the mean tip angle (related to canopy N-status) output by the instrument. For the early measurements included here the CAI values are sufficiently close to green LAI.
  • ViScan radiometer developed at research Centre Foulum (Thomsen et al. 2002). The hand carried ViScan radiometer is used for measuring the spectral reflectance of crop canopies. Spectral reflectance especially in the form of a spectral index calculated from two or more spectral bands (Broge and Leblanc, 2001) is closely related to e.g. green leaf area index and canopy chlorophyll content (Broge and Mortensen, 2002). The simple ratio vegetation index, RVI (Broge and Thomsen, 2002), calculated as the ratio of near infrared (780 nm) and visible red (660 nm) reflectance values, was used here as indicator of canopy green leaf area and chlorophyll content (N-status).
  • SPAD-502 chlorophyll meter from Konica Minolta. SPAD measurements are made manually by placing a leaf in a clip. Meter readings are related to the chlorophyll concentration in the leaf (Broge and Mortensen, 2002). 30 individual readings were made in each plot on the upper fully extended leaves in the canopy and averaged to a mean value by the instrument. Instrument readings were used as index values and not calibrated into absolute chlorophyll content.
  • The MobilLas sensor includes the following major hardware components (Thomsen and Schelde, 2007): a) Near-infrared laser range finder, AccuRange 4000, with high-speed interface produced by Acuity Research Inc., CA, USA. Range finder configured for close range, narrow beam (0.5 mm) and daylight operation. b) Two four-band radiometers, SKR 1850, produced by Skye Instrument Ltd., UK. Radiometers filtered  (650, 710, 730 and 780 nm) for the measurement of common spectral indexes (RVI, NDVI etc.) and red edge position (Broge and Leblanc, 2001; Thomsen et al., 2002; Broge et al., 2002). c) Global positioning sensor, GPS 16, produced by GARMIN International Inc., KS, USA.

Due to errors in delineation of some of the plots at Nissumgård in 2006, measurements of ViScan and MobilLas were not performed in 22 plots on any of the measurement dates in 2006. Due to data storage problems measurements of crop canopy reflectance using ViScan from 31 May 2006 at Nissumgård were only available from 11 plots. The missing ViScan data were substituted by similar data measured using MobilLas.

2.6 Fungicide deposition on leaves and soil

Deposition of spray liquid was measured on the crop and at the soil surface. A tracer, brillantsulfoflavin, was used to quantify the amount of spray liquid and hence fungicide deposited on the crop and at soil level. Brillantsulfoflavin is a stable product at 5 °C and storage for several months did not cause loss of activity (Jensen and Spliid, 2003). The tracer at a concentration of 100 g ha-1 brillantsulfoflavin was added to the spray solution in treatments with the lowest fungicide dose. This means that deposition was measured in the combinations N strategy ´ replicates giving a total of 40 plots per location. Before application of tracer and fungicide mixture in the field experiment, fluorescence interactions between fungicide and tracer was tested without revealing any problems.

Shortly before the experimental applications were carried out, objects were placed at soil level in order to collect the spray used for quantification of soil deposits. Rectangular filter paper objects with a size of 1.8 ´ 12 cm were used. This size allows a representative sampling, as the objects could reach from the middle of one plant row to the middle of the next row. The paper objects were placed on metal rods in order to avoid contamination with soil and in order to achieve a horizontal placement. Eight paper objects were placed in each plot. After the fungicide treatment was carried out, the paper objects were collected with two samples each consisting of four paper objects per plot. The filter papers were stored in 100 ml amber glass bottles under dark conditions at 5 oC until the samples were analysed. The tracer was solved in 50 ml demineralised water and the bottles were shaken thoroughly and a small proportion of the liquid was used for the analysis. Samples of the spray liquid were taken and stored the same way.

After the fungicide treatment, 9 crop plants from each plot was taken and divided into three sections: 1) 1st leaf (flag leaf), 2) 2nd leaf and 3) 3rd leaf. These plant samples were collected in plastic bags and after transportation stored at 5 °C. The tracer was solved using 100 ml demineralised water and the samples were shaken gently in order to avoid fluorescent material from the leaves. The liquid with tracer and fungicide was collected and stored dark at 5 °C until the analysis of tracer. The leaf area of each section was determined using a Licor Area Meter (model 3100). Following this the dry weight of the leaf sections were determined by drying at 80 °C for 24 hours.

The concentration of tracer in the liquid samples was determined using a Perkin Elmer model LS50B luminescence spectrometer. The bottles were shaken and a sample of 6 ml was used in the fluorescence detector. The sample was excited at a wavelength of 420 nm and after excitation emission was measured at 518 nm. The content of the sample was quantified using a number of standard concentrations ranging from 10 to 2000 mg l-1. From the concentration of brillantsulfoflavin in the sample the actual amount of tracer on the paper objects and on the leaf sections were calculated. For control purposes tracer concentration was also determined in the remaining spray solution from the experimental sprayer. Paper objects and leaf samples from untreated control were also washed with demineralised water and tested.

2.7 Overview of measurement dates

The measurements of crop characteristics were coordinated, so that the different measurement could be compared. However, due to weather conditions and time required for taking measurements, not all measurements could be performed on the intended dates (Table 3).

Table 3. Overview of dates of crop measurements.

Measurement GS32 GS39 GS65 GS75
Nissumgård (2005)        
Disease 10-05 24-05 28-06 11-07
Plant sample   02-06    
Canopy height 12-05 06-06    
SPAD 12-05 06-06    
VIScan 12-05 01-06 22-06 04-07
LAI2000 12-05 01-06 22-06 04-07
MobilLas 12-05 01-06    
Schackenborg (2005)        
Disease 10-05 24-05 24-06 07-07
Plant sample   30-05    
Canopy height   27-05    
SPAD 11-05 26-05    
VIScan 11-05 27-05 20-06 30-06
LAI2000 11-05 26-05 20-06 30-06
MobilLas 11-05 27-05    
Nissumgård (2006)        
Disease 17-05 31-05 22-06 11-07
Plant sample   31-05    
SPAD 23-05 31-05    
VIScan 23-05 31-05 20-06 04-07
LAI2000 23-05 01-06    
MobilLas 23-05 31-05    
Nissumgård (2006)        
Disease 18-05 31-05 22-06 11-07
Plant sample   31-05    
SPAD 17-05 31-05    
VIScan 17-05 31-05 20-06 04-07
LAI2000 17-05 01-06    
MobilLas 17-05 01-06    

2.8 Experiment with fungicide deposition at different driving speed

In 2006 a supplementary experiment examining the influence of speed of the sprayer on deposition on leaves and soil was carried out. The experiment was carried out in winter wheat crop at Research Centre Flakkebjerg. The variety was Robigus and a two-factorial field experiment was conducted with the following factors:

Factor 1. Driving speed and application technique:

  1. 4 km h-1, Low drift LD-02 nozzle at 240 L ha-1

  2. 8 km h-1, Low drift LD-02 nozzle at 120 L ha-1

Factor 2. Nitrogen application rate:

  1. 80 kg N ha-1

  2. 160 kg N ha-1

Nitrogen was applied as a single application on 18 April at both N rates. A randomised block design with 4 replicates and a plot size of 2.5 ´ 10 m was used. At 4 km/h the spray liquid consisted of tap water with addition of the tracer Rhodamin B (100 g ha-1) and a non-ionic surfactant at a concentration of 0.1%. Another tracer, Brillantsulfoflavin (100 g ha-1) was used at 8 km/h and a non-ionic surfactant was again used at a concentration of 0.1%. The surfactant used was a linear alcohol polyethoxylate (Lissapol Bio, Syngenta). The purpose of the surfactant was to give the spray liquid properties that are comparable to a spray liquid with a fungicide. The experimental treatment was carried out at growth stage BBCH 53 when the winter wheat was 75 cm high. Deposition of spray liquid was measured on 1) 1st leaf (flag leaf), 2) 2nd leaf and 3) 3rd leaf and at soil level using the same methodology as described in section 2.6. The concentration of Rhodamin B was also measured on the Perkin Elmer luminescence spectrometer. Rhodamin B was chosen as this tracer was found to interact limited with brillantsulfoflavin and has its fluorescence peak at another wavelength. Measuring Rhodamin B concentration, the sample was excited at a wavelength of 553 nm and after excitation emission was measured at 578 nm.

2.9 Statistical analyses

The plot level data were analysed using the ANOVA, GLM and MIXED procedures in the SAS system (SAS, 1996). In the general linear model, the interaction term block ´ nitrogen was used in the denominator of the F-test corresponding to the factor nitrogen, while the residual error was used for F-tests for differences between fungicide treatments and the interaction term nitrogen ´ fungicide. In the mixed models, the whole plot term (block ´ nitrogen) and blocks were having random effects, and the other factors had fixed effects. Satterthwaites method was used for calculating denominator degrees of freedom in the mixed models.

Correlation and regression analyses on the sensor measurements were performed using the CORR and REG procedures of the SAS system (SAS, 1996).

Regression models were compared in terms of the multiple correlation coefficient (R²) and the root means squared error (RMSE) of the model residuals.

 



Version 1.0 January 2008, © Danish Environmental Protection Agency