Benghal dayflower, also known as tropical spiderwort, is a noxious, invasive annual/perennial weed that has become one of the most troublesome species in agronomic crop production systems in the southeastern United States (Webster and Sosnoskie, 2010). Benghal dayflower is native to tropical Asia and Africa and is listed among the world’s worst weeds (Holm et al., 1977). Benghal dayflower was not considered a common or problematic weed in the U.S. until the early 2000s, when it was confirmed in 12 counties in Florida and 29 counties in Georgia (Prostko et al., 2005). Over the past two decades, the species has spread rapidly and become a significant weed across much of the southeastern United States, including Alabama, Florida, Georgia, North Carolina, South Carolina, and Virginia (USDA, 2020; Webster and Sosnoskie, 2010; Webster and Nichols, 2012). The spread of Benghal dayflower has been associated with the shift to minimum-tillage production systems, the introduction and widespread adoption of glyphosate-resistant crops, and the concomitant increase in glyphosate use (Leon et al., 2022). Benghal dayflower is tolerant to glyphosate; therefore, its survival and reproduction increases after glyphosate eliminates competition from other weeds (Price et al., 2009).

Benghal dayflower is particularly difficult to control due to its unique biological characteristics, which include reproductive flexibility (producing seeds both above and below ground and the ability to exist as an annual or perennial depending on climate), a late and prolonged emergence period that extends beyond preplant tillage and early-season weed control, high seed production (>1,600 seeds per plant), and a sprawling growth habit that forms dense mats and develops adventitious roots at the nodes (Holm et al., 1977; Prostko et al., 2005; Walker and Evenson, 1985a, b). Growers in the southeastern United States are facing an ever-increasing challenges in controlling Benghal dayflower because of limited effective herbicide options. Furthermore, its ability to reproduce vegetatively and regenerate from cut stems undermines mechanical control efforts (Budd et al., 1979), while light cultivation can fragment and disperse stems, potentially increasing the extent of infestation (Daramola et al., 2021).

Poor control of Benghal dayflower in glyphosate-tolerant crops like cotton, corn, and soybean can increase infestations in subsequent rotational crops like peanut, which is a weak competitor due to its low, spreading growth habit (Chaudhari et al., 2018). Benghal dayflower has been shown to be more competitive than peanut (Chivinge and Kawisi 1990), reducing yield by 10% within four weeks of interference and causing over 50% yield loss with season-long competition (Webster et al., 2007). Effective management strategies are therefore essential to minimize interference and yield loss associated with Benghal dayflower.

Although cultural practices like deep tillage, early planting, narrow spacing, and twin-row spacing can help suppress Benghal dayflower, they are not sufficient alone to protect peanut yield (Daramola et al., 2024a; Ferrell et al., 2020; Stephenson and Brecke, 2011). Effective control of troublesome weeds often requires timely herbicide programs with tank mixtures involving multiple modes of action (Norsworthy et al., 2012). Integrating residual preemergence herbicides with effective postemergence options is also essential for the management of problematic weeds (Kumar and Jha, 2015). Previous research shows inconsistent control of Benghal dayflower with preemergence herbicides with single modes of action. For example, Benghal dayflower control with preemergence application of flumioxazin (0.072 kg ai ha^-1), fluometuron (1.12 ka ai ha^-1), norflurazon (1.507 kg ai ha^-1), prometryn (0.048 kg ai ha^-1) and pyrithiobac (0.048 kg ai ha^-1) was only 24% to 67% (Webster et al., 2006). Only S-metolachlor at 1.0 and 1.6 kg ai ha⁻¹, provided >80% control of Benghal dayflower (Webster et al., 2006). Among postemergence herbicide programs evaluated for Benghal dayflower control, only paraquat combined with S-metolachlor or bentazon provided >90% control (Daramola et al. 2024a; Stephenson and Brecke, 2011). However, paraquat use is limited to within 28 days after peanut emergence, which is often before the peak emergence of Benghal dayflower in early July. Additionally, paraquat may cause crop stunting and foliar injury, which can result in yield reduction under stress conditions (Brecke et al. 1996; Daramola et al. 2024b). There is limited information on alternative herbicide options for effective Benghal dayflower control in peanut. Therefore, preemergence and postemergence fallow experiments were conducted to evaluate the performance of alternative (non-S-metolachlor and non-paraquat) herbicides labeled for use in peanut for Benghal dayflower control. Since most peanut growers rely on herbicide mixtures for broad-spectrum weed control, this study evaluated diclosulam (WSSA Group 2) and flumioxazin (WSSA Group 14) preemergence mixtures, along with various postemergence herbicide programs.

Field experiments were conducted in 2022 and 2023 at the West Florida Research and Education Center, University of Florida, Jay, FL (30˚46′29.5″ N; 87˚08′19.9″ W), on a Red Bay sandy loam soil (fine-loamy, kaolinitic, thermic Rhodic Kandiudults) with pH 5.8 and 2.1% organic matter. Trials were established in a crop-free area with heavy natural infestation of tropical spiderwort. Herbicides labeled for use in peanut were applied at recommended rates and timings (Table 1). Weather data, including weekly rainfall after preemergence application, cumulative monthly rainfall, and average monthly temperatures, are presented in Figure 1.

Separate preemergence and postemergence experiments were arranged in a randomized complete block design with four replications. Plot size was 7.6 m × 3.6 m. Treatments were applied using a CO₂-pressurized backpack sprayer with TTI11002 nozzles, calibrated to deliver 140 L ha⁻¹ at 4.8 km hr⁻¹. Paraquat was applied at 0.25 kg ai ha^-1 to control emerged vegetation prior to the time of preemergence herbicide application. Preemergence herbicide treatments included diclosulam plus pendimethalin, diclosulam plus fluridone, diclosulam plus flumioxazin, diclosulam plus dimethenamid-P, diclosulam plus S-metolachlor, flumioxazin plus S-metolachlor, flumioxazin plus dimethenamid-P, flumioxazin plus fluridone, and S-metolachlor plus fluridone. An untreated control was included for treatment comparison. Applications were made on July 15, 2022, and July 14, 2023, to align with peak Benghal dayflower emergence. Fields were rainfed, and at least 3.5 cm of rainfall occurred within 7–10 days after treatment each year (Figure 1), ensuring herbicide activation.

Postemergence herbicide treatments were applied when Benghal dayflower plants were 10–20 cm tall at a density of 80–150 plants m⁻². Treatments included paraquat plus bentazon plus S-metolachlor, paraquat plus bentazon plus Anthem Flex (pre-mix carfentrazone-ethyl:pyroxasulfone), paraquat plus S-metolachlor plus Storm (pre-mix acifluorfen:bentazon), diclosulam plus S-metolachlor, imazapic plus S-metolachlor plus 2,4-DB, imazapic plus pre-mix carfentrazone-ethyl:pyroxasulfone, imazapic plus pre-mix carfentrazone-ethyl:pyroxasulfone plus S-metolachlor, imazapic plus pre-mix acifluorfen:bentazon plus S-metolachlor, acifluorfen plus S-metolachlor plus 2,4-DB, chlorimuron ethyl plus S-metolachlor plus 2,4-DB, and pre-mix acifluorfen:bentazon plus 2,4-DB. An untreated control was included for treatment comparison. All postemergence herbicide treatments included a nonionic surfactant (NIS 0.25% v/v; Preference, Winfield Solutions, York, PA) and were applied on July 24, 2022, and July 27, 2023.

Visual control ratings were recorded at 28, 42, and 56 days after treatment (DAT) for the preemergence experiment, and at 28 and 56 DAT for the postemergence experiment. Benghal dayflower density and biomass were assessed at 42 and 56 DAT for the preemergence treatments, and at 56 DAT for the postemergence treatments. Weed control was visually estimated on a scale from 0% (no control) to 100% (complete mortality), relative to the untreated control. Density was measured from two 1 m² quadrats per plot, and aboveground biomass was collected from the same quadrats. Samples were dried in a forced-air oven at 60°C for one week, and dry weights recorded. Density and biomass reductions were calculated relative to the untreated control using the formula:

Reduction (%) = [(A – B) / A] × 100

where A is the density or biomass of the untreated control, and B is the density or biomass of the treated plot.

Data were analyzed using ANOVA with PROC GLIMMIX procedure in SAS version 9.4 (SAS Institute Inc., 2012). Initial analyses evaluated year as a fixed effect. Since the treatment × year interaction was not significant, data from both years were pooled, with year treated as a random effect in subsequent analyses. Benghal dayflower control, density reduction, and biomass reduction data were arcsine square-root transformed prior to analysis to meet assumptions of normality. Means were separated using Tukey’s Honest Significant Difference (HSD) test at P < 0.05. For presentation, means were back-transformed to percentage values.

Effective Benghal dayflower control 56 DAT is possible with preemergence application of diclosulam plus dimethenamid-P, diclosulam plus flumioxazin, diclosulam plus S-metolachlor, flumioxazin plus dimethenamid-P, flumioxazin plus S-metolachlor, and fluridone + S-metolachlor. While combinations like diclosulam plus fluridone, diclosulam plus pendimethalin, and flumioxazin plus fluridone provided good early-season control (28 DAT), they failed to maintain control due to the continuous emergence of Benghal dayflower. Season-long control of Benghal dayflower will require a multi-component approach that integrates effective preemergence with timely postemergence herbicide treatment. Among the eleven postemergence herbicide programs evaluated, only those including paraquat, specifically: paraquat plus bentazon plus S-metolachlor, paraquat plus bentazon plus premix carfentrazone-ethyl:pyroxasulfone, and paraquat plus S-metolachlor + premix acifluorfen:bentazon maintained >85% control from 14 to 56 DAT. While imazapic-based programs provided early suppression, their control dropped significantly by 56 DAT, especially when Benghal dayflower exceeded 10 cm in height. In summary, optimal Benghal dayflower control in peanut requires a residual S-metolachlor-based preemergence herbicide followed by timely postemergence applications, with paraquat plus bentazon plus S-metolachlor identified as the most effective option for season-long management.