Weed Science - University of Wisconsin

Predicting Longterm Giant Foxtail and Velvetleaf Populations

C.M. Boerboom and A.J. Bussan*

Introduction

The high cost of herbicide programs in corn and soybeans has created an interest in using reduced herbicide rates to lower production costs. The successful use of reduced herbicide rates in Wisconsin and the associated management considerations have been summarized previously (Doll et al. 1992, Proost et al. 1996). Unfortunately, most of the research in Wisconsin has focused on the use of preemergence-applied herbicides in corn. While other states have extensively researched postemergence herbicide use in soybeans (Defelice and Kendig 1994), less research on reduced rates of postemergence herbicides has been conducted in Wisconsin, especially in corn. Therefore, we conducted a two year study to determine how effective reduced postemergence herbicide rates were in Wisconsin corn and soybeans (Bussan and Boerboom 1997). Still, many farmers are concerned that using reduced herbicide rates may leave a few escaping weeds and that these escapes will lead to increased weed problems in the future. Therefore, we also wanted to be predict what the long-term impact of using reduced rates of postemergence herbicides would be on future weed populations.

Computer Simulation Model

To make these predictions, we needed to develop a computer simulation model that would, in essence, be able to accurately "grow" a weed through an entire season and then repeat it for several cycles into the future. This requires weed information such as the percent emergence from the seedbank, the percent surviving the herbicide, the seed production and biomass of the survivors, the effect of weed density on survival, seed production, and biomass, and the survival of seed returning to or already in the seedbank. These factors vary by weed, tillage, herbicide, and crop. Therefore, we focused specifically on modeling giant foxtail, controlled with Accent and Poast Plus, and velvetleaf, controlled with Banvel and Pursuit, in corn and drilled soybeans. The herbicide rates ranged from 0 to the full labeled rate (the proportion of the full rate is described below as 1x, 1/2x, etc.). Other details about the study and single year results were reported at the conference last year (Bussan and Boerboom 1997). Information on factors such as emergence, seed decay, and predation were obtained from the literature.

All of the following results are based on the scenario of a corn-drilled soybean rotation under reduced tillage and that the same rate of herbicide is used in both crops. The postemergence herbicides were applied at an early timing as recommended when using reduced herbicide rates. Because it is also recommended that mechanical weed control should be used when herbicide rates are reduced, we also included mechanical treatments in some predictions. The mechanical treatments were cultivation in corn and rotary hoeing in the drilled soybean. Each model simulation was run for a 20-year time period and all of the results are based on the total of 20 separate runs. The results were based on 20 runs because each run results in a unique prediction. This variation exists because the model can randomly use results from the range of weed survival, seed production, etc. that we measured in the field experiments. For example, we had more giant foxtail survivors and seed production in one year than the other year. In addition, the model selects from a range of values within that year. This variation makes the predictions more realist because the model may use several poor years in a sequence which gives a better perspective on the potential variation or risk.

Computer Simulation Predictions

 

Seedbank populations

The model starts with an initial seedbank level and the effect of the herbicide rate used on the weed population can then be predicted. Without any herbicide use, the giant foxtail seedbank quickly rises from 1,000 seeds/m 2 to a level that fluctuates between 5,000 and 10,000 seeds/m 2 (data not shown). In contrast, when postemergence herbicides were used at 1x rates, the seedbank was quickly depleted by 95% by 4 years (figure 1). As expected, the use of 1/2x rates alone were not as successful as 1x rates and had much more variation. Still, the seedbank was reduced, which suggests that while some giant foxtail were escaping treatment and producing seed, more seed was being lost because of seed decay and from controlled seedlings. However, mechanical treatments are recommended with reduced herbicide rates. When mechanical treatment was combined with 1/2x rates, the predicted result is very similar to the prediction with the 1x herbicide rate (figure 2). This supports the recommendation for using mechanical treatments with reduced herbicide rates and removes much of the risk.

Figure 1. Predicted giant foxtail seedbank in a corn-drilled soybean rotation.

Graph of the predicted giant foxtail seedbank

Figure 2. Predicted giant foxtail seedbank in a corn-drilled soybean rotation.

Graph of predicted giant foxtail seedbank with tillage

When the velvetleaf seedbank started at 100 seeds/m2 , the model predicted that the seedbank would increase to a level of about 4,000 seeds/m2 in 3 years if not controlled (data not shown). Besides herbicide rate, verticillium also significantly affected velvetleaf seed production. Because verticillium reduced seed production, the model predictions shown below were simulated without verticillium to present a worst case scenario. The control provided by the 1x herbicide rates are predicted to reduce the velvetleaf seedbanks, but not as rapidly as the 1x rates reduced the giant foxtail seedbanks (figures 1 and 3). This is expected because velvetleaf can remain viable in the seedbank longer than giant foxtail. The 1/2x herbicide rates only gradually reduced the seedbank (figure 3). However, when this reduced rate was supplemented by mechanical treatment, the seedbank was reduced more rapidly (figure 4). Still, there was more variation in the predictions among simulations, suggesting that using reduced rates with high velvetleaf densities may be more risky than with giant foxtail.
Figure 3. Predicted velvetleaf seedbank in a corn-drilled soybean rotation.

Graph of the predicted velvetleaf seedbank

Figure 4. Predicted velvetleaf seedbanks in a corn-drilled soybean rotation.

Graph of the predicted velvetleaf seedbank with tillage

Annualized net returns

The computer model also predicted the effect of any surviving giant foxtail or velvetleaf on crop yield. Therefore, the net returns (crop income less all weed control costs) could be determined for each year of a simulation. To simplify comparisons, the net returns were summarized as annualized net return (ANR), which accounts for interest over the 20 years. For giant foxtail, the ANR for the 1/2x herbicide rates either alone or with mechanical treatments was higher than the 1x herbicide rates because of the lower herbicide cost (figure 5). The additional cost for the mechanical treatments with the 1/2x rates was offset by slightly higher crop yields so that the ANR were nearly identical for 1/2x rates with or without supplemental mechanical treatments.

Figure 5. Predicted annualized net return of selected giant foxtail treatments.

Predicted annualized net return of selected giant foxtail treatments

The 1/4x rates combined with mechanical treatments also had high ANR because Accent and Poast Plus were quite effective when applied at early growth stages as in our field trials. For giant foxtail, the ANR for the 1/2x rates were also greater than for the 1x rates regardless of the initial foxtail density. In contrast, the results for velvetleaf varied depending on the starting density. At lower densities, the ANR for the 1/2x rates were greater than the ANR for the 1x rates (figure 6). At high densities, this advantage is eliminated.
Figure 6. Predicted annualized net return of selected velvetleaf treatments.

Predicted annualized net return of selected velvetleaf treatments

Treatment thresholds.

The simulation model also allowed thresholds to be studied. After several years of good control, there would be years when densities would be below threshold levels. For example, if giant foxtail was not sprayed at densities below 1 weed/m2 , the foxtail density would call for treatment in most years. However, when not treated, the seed produced would increase the seedbank and require herbicide treatment in subsequent years (figure 7). This shows the long-term consequences that need to be considered for thresholds. The threshold that maximizes ANR over time is called the economic optimum threshold (EOT). For giant foxtail, the predicted EOT is very low and in the range of 0.1 to 0.2 seedlings/m2 when mechanical treatments are never used and about 0.7 seedlings/m2 when mechanical treatments are always used (figure 8). The EOT was about 0.5 velvetleaf/m2 and was similar whether or not mechanical treatments were used (figure 9). For either weed, the EOT was similar for 1x and 1/2x herbicide rates.

Figure 7. Giant foxtail seedbank with a threshold of 1 giant foxtail
per m
2 while using 1x herbicide rates.

Graph of the giant foxtail seedbank

Figure 8. Predicted annualized net return as giant foxtail threshold density increases.

Graph of the predicted annualized net return as giant foxtail threshold density increases

Figure 9. Predicted annualized net return as velvetleaf threshold density increases.

Graph of the predicted annualized net return as velvetleaf threshold density increases

Conclusions

The predictions made by this computer simulation model should provide added confidence to those wishing to use reduced postemergence herbicide rates when supplemented with mechanical treatments in fields with low or moderate weed densities. The model predicts that if some giant foxtail or velvetleaf escape control with reduced rates, the weed populations will not explode in subsequent years. Therefore, if management allows for proper herbicide timing and follow-up cultivation, the risk should be minimal. Of course, if the reduced herbicide rate application can not be made to small weeds, the herbicide rate can be increased and not increase the risk for the farmer. However, the model also realistically predicts that reduced rates are not economically justified for higher velvetleaf densities. This confirms previous recommendations that reduced herbicide rates should not be used on high weed densities or difficult to control weeds.

Literature Cited

Bussan, A.J. and C.M. Boerboom. 1997. Effect of reduced herbicide rates on velvetleaf and giant foxtail survival and seed production. Proc. 1997 Wisconsin Fert., Aglime and Pest Management Conf. pp. 84-87.

Doll, J., R. Doersch, R. Proost, P. Kivlin. 1992. Reduced herbicide rates: aspects to consider. Univ. Wisconsin Extension Bull. A3563.

Defelice, M. and A. Kendig. 1994. Using reduced herbicide rates for weed control in soybeans. Univ. Missouri Extension Bull. MP686.

Proost, R.T., P.T. Kivlin, K.B. Shelley, and K.A Talarczyk. 1996. A summary of six years of on-farm demonstrations focusing on reduced preemergence herbicide rates. Proc. 1996 Wisconsin Fert., Aglime and Pest Management Conf. pp. 179-182.

*Former Graduate Student.

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