Sequential Applications of Synthetic Auxins and Glufosinate for Escaped Palmer Amaranth Control

Field and greenhouse studies were conducted to investigate the influence of sequence and timing of synthetic auxins and glufosinate on large Palmer amaranth (Amaranthus palmeri) control. Field studies were performed in Henry County, AL where treatments were applied to Palmer amaranth with average heights of 37 and 59 cm in 2018 and 2019, respectively. Sequential applications of 2,4-D/dicamba + glyphosate followed by (fb) glufosinate at labeled rates 3 or 7 days after initial treatment (DAIT) were used in addition to the reverse sequence with a 7-day interval. Time intervals of 3 or 7 days between applications did not influence Palmer amaranth control. Palmer amaranth was controlled 100% by dicamba + glyphosate fb glufosinate and 2,4-D + glufosinate fb glufosinate 7 DAIT in 2018. However, herbicide performance was reduced due to delayed application and taller plants in 2019 with up to 23% less visual injury. To further investigate Palmer amaranth response to dicamba and glufosinate applied sequentially, a greenhouse study was conducted in 2019 where physiological measurements were recorded over a 35-day period. Treatments were applied to Palmer amaranth averaging 38 cm tall and included dicamba + glyphosate fb glufosinate 7 DAIT, the reverse sequence, and a single application of dicamba + glufosinate + glyphosate. Glufosinate severely inhibited mid-day photosynthesis compared to dicamba with up to 90% reductions in CO2 assimilation 1 DAIT. In general, Palmer amaranth respiration and stomatal conductance were not affected by herbicides in this study. Applications of dicamba + glyphosate fb glufosinate 7 DAIT was the only treatment hindered Palmer amaranth regrowth with 52% reduction in leaf biomass compared to nontreated control. These data suggest Palmer amaranth infested fields are more likely to be rescued with sequential applications of synthetic auxins and glufosinate, but consistent control of large Palmer is not probable.


Introduction
Palmer amaranth (Amaranthus palmeri S. Wats) is a weed that remains at the center of row crop management concerns in the USA due to rapid growth and constant evolution of herbicide resistance. The dioecious growth habit and high fecundity associated with this weed are major factors responsible for the rate at which herbicide resistant populations have evolved and spread [1][2][3]. Even low Palmer amaranth density can lead to yield loss, reduced harvest efficiency, and accumulation of seeds in the soil [4][5][6]. Large plant height at maturity, high water use efficiency, drought tolerance mechanisms, and a C4 photosynthetic pathway provide Palmer amaranth with a competitive advantage over

Field Studies
Two non-crop studies were conducted at the Wiregrass Research and Extension Center in Henry County, AL (31 • 21 17.1" N 85 • 19 35.3" W) during summers of 2018 and 2019 in irrigated field with high Palmer amaranth pressure. The site included natural and augmented Palmer amaranth populations planted at 500 seeds m −2 on June 6 and May 10 in 2018 and 2019, respectively. Prior to seeding, the study area was disked thoroughly to remove existing weeds, then field cultivated to ensure smooth soil surface. An artificial population combined with existing population was established by spreading Palmer amaranth seeds sourced from peanut and cotton fields in Alabama with known glyphosate and ALS-inhibitor resistance. Mature female seed heads were collected in late September before crop harvest and cleaned by hand on Auburn University campus for Palmer seeds. Other weed species presented in the non-crop plots included morning glory (Ipomoea spp.), sicklepod (Senna obtusifolia), Florida pusley (Richardia scabra), Florida beggarweed (Desmodium tortuosum), and southern crabgrass (Digitaria ciliaris). The experimental design was a randomized complete block with four replications. Plot size was 3.3 m long by 3.3 m wide. Herbicide treatments and rates can be found in Table 1 (Table 1). Glyphosate was used in tank mixture with dicamba and 2,4-D choline to provide control of annual grass weeds and broadleaf weeds that are not resistant to glyphosate, which is a common practice for row crop farmers in the southeast US. It does not provide any control of resistant Palmer amaranth in this field. Initial herbicide applications were performed on 6 July and 12 June in 2018. A blanket application of S-metolachlor (Dual Magnum ® ; Syngenta Crop Protection, LLC, Greensboro, NC 67419, USA) was applied once 7 days after initial herbicide application at 1469 g ai ha −1 on all treated plots to limit Palmer amaranth seed germination later in the study, thus confounding ratings and data collection. Herbicides were applied to Palmer amaranth with average height of 37 and 59 cm tall in 2018 and 2019, respectively. All herbicides were applied with a CO 2 -pressurized backpack sprayer equipped with four TeeJet nozzles (TeeJet Technologies, Wheaton, IL 60187, USA) delivering 187 L ha −1 . Turbo TeeJet induction flat spray tips (TTI 110025, TeeJet Technologies, Wheaton, IL 60187,  USA) producing ultra-coarse droplets were used for treatments that included synthetic auxins to  reduce spray drift as label required, and Turbo TeeJet wide angle flat fan spray tips (TT 110025, TeeJet Technologies, Wheaton, IL 60187, USA) producing medium size droplets were used for glufosinate applications to increase spray coverage.
Palmer amaranth injury was visually estimated at 14 and 28 DAIT on a scale of 0 (no injury) to 100 (complete mortality). At 35 DAIT, ten Palmer amaranth heights were recorded randomly in each plot by measuring living individuals from the ground to the top of the plant. Palmer amaranth in each plot were cut at ground level 35 DAIT and immediately weighted to determine fresh biomass. Plants were only harvested from the middle area (2.4 × 2.4 m) in each plot to ensure adequate herbicide coverage was received.
Data were subjected to a mixed model analysis of variance through PROC GLIMMIX in SAS 9.4 (Statistical Analysis Systems ® , version 9.4; SAS Institute Inc., Cary, NC 27513, USA). Treatment and year were considered fixed effects, while block was a random effect and all interactions were examined. If treatment by year interactions were observed, data was analyzed separately to show individual effects for each year. Means comparisons were generated using Tukey's Honest Significant (HSD) different test with p = 0.05.

Greenhouse Study
In order to better understand Palmer amaranth physiological response to synthetic auxins and glufosinate, an experiment was conducted in a greenhouse with natural daylight at Auburn University in Auburn, AL during June of 2019. Temperatures ranged between 20 and 31 • C throughout the course of the study. Glyphosate and ALS-inhibitor resistant Palmer amaranth seed collected from Headland, AL were planted in 4 L pots filled with commercial potting soil (Miracle-Gro ® Moisture Control ® Potting Mix, The Scotts Company LLC, Marysville, OH 43040, USA). Plants were thinned to two plants per pot and grown until reaching 30 to 45 cm in height with irrigation and fertilizer applied as needed. One leaf on each plant was tagged with plastic string at the petiole, representing a young fully developed leaf (3-4 node position from the tip), to ensure the same leaf was measured throughout the study.
The experimental design was a randomized complete block with three replications in two separate runs. In addition to a nontreated control, treatments included a tank mixture of dicamba + glufosinate + glyphosate, dicamba + glyphosate fb glufosinate 7 DAIT, and glufosinate fb dicamba + glyphosate 7 DAIT. Reduced herbicide rates relative to the field study were chosen to allow Palmer amaranth survival and enable for physiological measurements up to 35 d after initial treatments. Dicamba, glufosinate, and glyphosate were applied at 186, 198, and 514 g ai ha −1 . Herbicides were applied using a CO 2 -pressurized backpack sprayer equipped with two flat fan 110,025 nozzles delivering 187 L ha −1 . Dicamba was applied with Turbo TeeJet induction flat fan nozzles (TTI110025, TeeJet Technologies, Wheaton, IL 60187, USA) and glufosinate with Turbo TeeJet wide angle flat fan nozzles (TT110025, TeeJet Technologies, Wheaton, IL 60187, USA).
Physiological measurements were recorded at 1, 3, 6, 8, 11, 13, and 35 DAIT. Measurements included mid-day photosynthesis, leaf stomatal conductance, and respiration, collected with a LI-6400XT (LI-COR Biosciences, Lincoln, NE 68504, USA). Before each midday photosynthesis measurements, light intensity in the greenhouse was recorded by a photosynthetic photon flux density meter (LI-190; LICOR Biosciences, Lincoln, NE, USA), temperature was monitored by an onsite weather station, and relative humidity was maintained between 60% and 70%. Conditions in the leaf cuvette were then set to match ambient environmental conditions, with the [CO 2 ] in the cuvette set to match ambient [CO2] (~410 ppm). The methodology for respiration measurements was the same but the light intensity was set to 0 µmol mol −1 . Photosystem II (PSII) quantum yield was recorded with a portable fluorometer (FluorPen FP 100, Photon Systems Instruments, Albuquerque, NM, USA 87106). Photosynthesis and stomatal conductance measurements were recorded at solar noon (11:00-13:00) while respiration and PSII quantum yield measurements were collected from dark-adapted plants two hours after sunset. At the end of physiological measurements, all Palmer amaranth leaves were removed at the petiole base 14 DAIT, fresh weight was recorded, then leaves were processed through a LI-3100C area meter (LI-COR Biosciences, Lincoln, NE 68504, USA) to determine total leaf area. Palmer amaranth bare stalks were allowed to resume growth until 35 DAIT when photosynthesis, respiration and fluorescence measurements were repeated as indicated above, and leaves were removed at the petiole base once more and weighted.
Each physiological measurement was averaged across the two tagged leaves per pot and data was subjected to a mixed model analysis of variance through PROC GLIMMIX in SAS ® 9.4 (Statistical Analysis Systems ® , version 9.4; SAS Institute Inc., Cary, NC 27513, USA) with treatment considered as a fixed effect. Data were pooled across experiment repetitions which was considered a random variable. Scatter plots were generated in Sigmaplot 13.0 (Systat Software, San Jose, CA 95131, USA) and means comparisons were generated using Tukey's HSD test with p = 0.05.

Field Study: 2,4-D Choline-Based Programs
A year by treatment interaction was observed for Palmer amaranth control 14 DAIT, height, and biomass for 2,4-D based programs. No interaction was observed for Palmer amaranth control 28 DAIT; therefore, data were combined across years for 28 DAIT (Tables 2 and 3). Paul, MN 55164, USA). C Abbreviation: DAIT, days after initial treatment. D Visual injury estimated on a scale of 0% (no injury) to 100% (complete mortality). E Means within a column followed by the same letter do not differ significantly at p = 0.05 based on Tukey's HSD. F A treatment by year interaction was observed for Palmer amaranth control 14 DAIT at p = 0.05; therefore, data were analyzed and presented separately for each year. G No treatment by year interaction was observed for Palmer amaranth control 28 DAIT at p = 0.05; therefore, data were combined across years to show treatment effects.
All 2,4-D and glufosinate combinations where 2,4-D was included in initial applications provided statistically similar control 28 DAIT, ranging from 80 to 93%. In comparison, sequential applications of glufosinate or glufosinate fb 2,4-D + glyphosate resulted in significantly lower control 28 DAIT of 68% and 76%, respectively. Time intervals of 3 and 7 d did not influence the level of control of 2,4-D + glyphosate fb glufosinate at 14 and 28 DAIT. Similar to this study, Merchant et al. [19] observed poor Palmer amaranth control at cotton layby (79%) with sequential glufosinate applications at 471 g ai ha −1 spaced 15 d apart but reported at least 95% control when 2,4-D at 1120 g ai ha −1 was mixed with glufosinate at each application. Craigmyle et al. [25] also reported 19% higher control of Amaranthus sp. 30 to 35 cm tall with sequential applications of 2,4-D + glufosinate at 1.12 and 0.45 kg ai ha −1 , respectively, as opposed to glufosinate alone. Data from these studies suggested sequential applications of glufosinate alone or glufosinate applied before 2,4-D are not sufficient for controlling large Palmer amaranth. Greater Palmer amaranth control was achieved by either applying 2,4-D before glufosinate, or by applying both 2,4-D and glufosinate in a tank mixture fb either 2,4-D or glufosinate or combination of the two 3 or 7 days later. With exception of 2,4-D + glufosinate fb glufosinate 7 DAIT which resulted in 100% control in 2018, Palmer amaranth height was similar for all other treatments in 2018 and 2019 (Table 3). All treatments resulted in significantly reduced plant height and biomass relative to the nontreated control for 2018 and 2019. Herbicide treatments did not differ significantly in terms of Palmer amaranth biomass in 2018, which ranged from 0 to 2972 kg ha −1 for treated plots. Treatments of 2,4-D + glufosinate fb glufosinate and 2,4-D + glufosinate fb 2,4-D + glufosinate tank mixtures resulted in the greatest reductions of biomass and height in 2018 as compared to the nontreated control. Applications of 2,4-D + glyphosate fb glufosinate 3 DAIT and 2,4-D + glufosinate fb 2,4-D + glufosinate produced the lowest Palmer height and biomass, respectively, in 2019. Poor Palmer amaranth control in 2019 was observed in terms of biomass as all treatments resulted in 1250 kg ha −1 or greater biomass, due to delayed application and larger size of Palmer at herbicide application.

Field Study: Dicamba-Based Programs
No treatment by year interaction was observed for Palmer amaranth control 14 DAIT. However, a treatment by year interaction was observed for control 28 DAIT, height, and biomass at p = 0.05. Therefore, data was presented by year for those datasets. Glufosinate applied sequentially provided statistically similar control 14 DAIT as dicamba + glyphosate fb glufosinate 3 or 7 DAIT and dicamba + glyphosate fb dicamba + glyphosate 7 DAIT (Table 4). Palmer amaranth control of these dicamba based programs ranged from 79 to 94%. Glufosinate applied 7 d before dicamba + glyphosate resulted in the lowest Palmer amaranth control 14 DAIT at 77%. Sequential applications of dicamba + glyphosate fb glufosinate provided at least 87% control 14 DAIT regardless of the time interval tested. Treatments of dicamba + glyphosate fb glufosinate 7 DAIT resulted in complete mortality by 28 DAIT whereas the reverse sequence resulted in 70% control in 2018. However, control at 28 DAIT was variable among years and all dicamba based programs performed similarly in 2019. Programs of glufosinate fb glufosinate or glufosinate fb dicamba + glyphosate 7 DAIT did not adequately control Palmer amaranth 28 DAIT in either year with ratings of 78 and 57% in 2018 and 2019, respectively. Dicamba + glyphosate fb either glufosinate 3 DAIT or dicamba + glyphosate again 7 DAIT produced better Palmer control (32 and 34% respectively) than glufosinate fb glufosinate treatment at 28 DAIT in 2019. Randell et al. [31] observed less than 90% Palmer amaranth control with sequential glufosinate applications at 660 g ai ha −1 spaced 10 to 14 d apart which resulted in 20,000 to 27,000 survivors ha −1 . These data suggest addition of auxin herbicide should be considered in dicamba and 2,4-D tolerant crops to reduce the number of Palmer amaranth escapes and increase control efficacy on large Palmer amaranth as glufosinate alone can be unreliable when targeting larger weeds.
All dicamba programs resulted in significantly reduced Palmer amaranth height as compared to the nontreated control in 2018 and 2019 (Table 5). All herbicide treatments resulted in plants at least 106 cm shorter than those in the nontreated control in 2018, with applications of dicamba + glyphosate fb glufosinate 7 DAIT resulting in complete mortality and no plant height could be measured. The greatest height reductions in 2019 were recorded in plots treated with dicamba + glyphosate fb glufosinate 3 DAIT and dicamba + glyphosate fb dicamba + glyphosate 7 DAIT, which were 100 and 101 cm lower than nontreated control respectively. Biomass reductions produced by dicamba + glyphosate fb glufosinate 7 DAIT did not differ significantly from the other treatments, although total control was observed with this treatment in 2018. All other treatments reduced biomass by at least 10,000 kg ha −1 relative to nontreated control in 2018. With exception of glufosinate fb dicamba + glyphosate 7 DAIT, all treatments were lower than 1000 kg ha −1 . The same level of performance was not observed in 2019 and all treatments produced statistically similar amount of biomass ranged from 3265 to 5920 kg ha −1 . Sequential applications where dicamba + glyphosate was applied before glufosinate resulted in Palmer amaranth biomass of 0 to 403 and 3784 to 5920 kg ha −1 in 2018 and 2019, respectively, which were not significantly better than glufosinate sprayed twice or glufosinate fb dicamba + glyphosate. Vann et al. [21] demonstrated that salvage programs can be effective in Xtendflex cotton TM (Monsanto Co, St. Louis, MO 63167) with sequential applications of dicamba + glufosinate combined with a layby application of diuron + MSMA which provided 94 to 99% control of Palmer amaranth, ranging in heights of 7 to 71 cm tall at the initial application. However, current labels do not allow dicamba and glufosinate tank mixtures and sequential applications will be the only option to utilize both herbicides in dicamba tolerant crops. These data suggest that dicamba applied before glufosinate may be more effective to control large Palmer amaranth than the reverse sequence. However, glufosinate fb dicamba programs and glufosinate fb glufosinate can still be considered viable options if weather conditions do not permit dicamba to be applied first, or in situation where Palmer amaranth size is smaller. Based on data generated from this study, consistent control of large Palmer amaranth is not guaranteed in either dicamba or 2,4-D resistant crops in rescue situations, and herbicide efficacy in rescue situations is subject to plant height and abiotic influences, thus may vary each year. Although new technology is available allowing broadcast applications of synthetic auxins and glufosinate in cotton and soybeans during the growing season, Palmer amaranth control can be variable among years and locations [19,24]. Herbicide efficacy can be significantly impacted by Palmer amaranth size, maturity, and growing conditions [23,[32][33][34]. Height and biomass of Palmer amaranth in this study was similar in nontreated control plots among years with heights averaging from 133 and 135 cm and biomass of 13,569 and 10,175 kg ha −1 at maturity in 2018 and 2019, respectively. However, herbicide performance was highly variable between years as Palmer amaranth heights at initial application ranged from 0 to 39 and 34 to 52 cm for all treatments in 2018 and 2019, respectively. These observations suggest plants received adequate time to reach maturity before collecting height and biomass data. Palmer amaranth height at initial applications was likely the greatest factor to influence the level of control observed. Palmer amaranth heights at initial applications had a greater impact on efficacy of dicamba-based programs than 2,4-D choline-based programs. In 2019, adverse weather conditions (rainy and windy days) prior to initial herbicide applications resulted in a substantial delay (8 days late) and allowed for additional Palmer amaranth growth. This occurrence is a frequent challenge for producers and plants can quickly exceed optimal heights for control with growth rates reported up to 5 cm per day [7,8].
Taller, more mature plants with a larger canopy can reduce herbicide coverage of lower leaves, potentially impacting glufosinate efficacy. Glufosinate is a contact herbicide which requires adequate coverage and absorption to be effective [35]. For these reasons, glufosinate applications are only recommended for plants smaller than 7.5 cm tall are not as effective on larger Palmer amaranth [27,[36][37][38]. Similarly, Cuvaca et al. [33] observed 7% reductions in dicamba absorption and 15% lower translocation in Palmer amaranth 30 cm tall as compared to 10 cm tall. Dicamba and 2,4-D are systemic herbicides and efficacy is dependent on translocation within the plant [35]. Larger plants may have thicker plant cuticles which could reduce herbicide penetration resulting in poor control [27,36,39]. Furthermore, mature plants have reduced sugar transport which may decrease translocation of some systemic herbicides [34,40,41]. Highest label rate of glufosinate (880 g ai ha −1 ) plus ammonium sulfate and application under optimal environmental conditions may be required to provide additional control of large Palmer amaranth plants [42,43].

Greenhouse Study
Glufosinate applications severely inhibited Palmer amaranth mid-day photosynthesis as compared to dicamba. Treatments in which glufosinate was applied initially reduced mid-day photosynthesis at least 90% 1 DAIT whereas dicamba applied initially only reduced photosynthesis 22% (Table 6). Photosynthetic rates improved over time and were not significantly different from the nontreated control by 8 DAIT. Dicamba + glyphosate fb glufosinate reduced photosynthesis by 84% compared to nontreated control 8 DAIT whereas glufosinate fb dicamba + glyphosate was similar to the nontreated control at that timing. No treatment differences in photosynthetic rates were observed 13 DAIT or in regenerated tissue 35 DAIT. Quantum yield of PSII followed similar trends as mid-day photosynthesis with the greatest immediate reductions observed for glufosinate applications, whether applied before, after, or tank mixed with dicamba + glyphosate. No statistical differences were observed for quantum yield of PSII for any treatment at and after 13 DAIT, suggesting PSII has returned to normal function. Similar to the mid-day photosynthesis measurements, the only treatment that resulted in reduced PSII quantum yield 11 DAIT was dicamba + glyphosate fb glufosinate 7 DAIT, potentially indicating slower Palmer amaranth recovery from this treatment.
Leaf stomatal conductance and photosynthesis were variable in the nontreated control at different measurement timings, likely impacted by daily changes in temperature and humidity (Table 6).
Treated Palmer amaranth did not result in reduced stomatal conductance relative to the nontreated control with exception of 1 DAIT where reductions of 67%, 46%, and 89% were observed for three-way mix, dicamba + glyphosate fb glufosinate, and glufosinate fb dicamba + glyphosate treatments, respectively. Similar to mid-day photosynthetic observations 1 DAIT, treatments with glufosinate applied first inhibited stomatal conductance at a greater magnitude as compared to dicamba + glyphosate applied first. Respiration measurements were likely confounded by tissue degradation resulted from glufosinate applications. Glufosinate is a contact herbicide that causes rapid defoliation which may have resulted in an excess of carbon dioxide release as opposed to carbon dioxide flux due to respiration [35]. This would explain the more negative respiration values observed 1 DAIT from glufosinate treatments as opposed to dicamba which is a synthetic auxin and does not induce rapid defoliation. Ammonium accumulation and stomatal closure have been suggested to cause rapid photosynthetic inhibition in Palmer amaranth treated with glufosinate in as little as 30 min after application [44]. However, the results of this study suggest stomatal conductance was not severely impacted by dicamba + glyphosate and glufosinate applied sequentially or in tank mixtures. The possibility exists that the combination of two herbicides with distinctly different modes of action may have interfered with transpiration processes.
Regrowth of Palmer amaranth is often a major concern associated with glufosinate applications as glufosinate does not prevent weed regrowth [26,27]. All treatments in this study resulted in similar and significantly lower leaf biomass and area 14 DAIT as compared to the nontreated control (Table 7).  When plants were allowed to continue growth over a three-week period following leaf removal 14 DAIT, the only treatment that resulted in significantly lower leaf biomass from growth was dicamba + glyphosate fb glufosinate 7 DAIT. These data suggest Palmer amaranth recovery may be impaired by application of dicamba + glyphosate fb glufosinate as compared to the reverse sequence or tank mixture, which has valuable implication for Palmer amaranth management in field. Coetzer et al. [45] showed that less than 2% of glufosinate is translocated outside of the leaf where it was applied. This observation illustrates the need for adequate coverage when applying glufosinate to larger plants with sizable canopy. Such a scenario may explain the lack of control 28 DAIT observed in the field for sequential glufosinate applications by itself, where rapid defoliation occurred but glufosinate was unable to kill large Palmer stem due to lack of coverage, thus allowing plant to regrow and recover from injury.

Discussion
Incorporation of multiple modes of action into weed control programs is frequently recommended by weed scientists to reduce Palmer amaranth survivors and delay evolution of herbicide resistance [8,46]. Results of this study suggest multiple applications of POST herbicides with different modes of action may increase control of large Palmer amaranth. Sequential applications of synthetic auxins fb glufosinate are more likely to rescue Palmer amaranth infested fields as opposed to the reverse sequence. Glufosinate alone applied sequentially did not adequately control large Palmer amaranth in either year of this study. Higher rate of glufosinate plus ammonium sulfate may be needed to enhance control efficacy when 2,4-D or dicamba cannot be utilized due to spray drift concern. Although some combinations of sequential applications of synthetic auxins and glufosinate were effective, herbicide applications to large Palmer amaranth (>10 cm) is not recommended and timely applications of POST herbicides remain the most effective approach. Although results found in this study indicate sequential applications of 2,4-D, dicamba and glufosinate may have potential to rescue infested fields, Palmer amaranth control was not consistent among years with different growing conditions, suggesting rescue practice should be avoided if possible. If salvage programs are utilized and fail, manual removal is required to limit seed return to the soil seed bank and reduce the risks of herbicide resistance development.

Conclusions
Field study confirmed that 2,4-D or dicamba sprayed in sequence with glufosinate provided better Palmer amaranth control than single application and two applications of glufosinate alone, regardless 3-or 7-days interval between applications. Palmer amaranth size at application plays a key role to achieving sufficient control. No treatment provided complete control of large Palmer (>30 cm) which indicated the importance of spraying timely. Data from greenhouse study glufosinate immediately reduced up to 90% mid-day photosynthesis in terms of CO 2 assimilation within 24 hrs. Palmer amaranth respiration and stomatal conductance were not affected by herbicides in this study. Dicamba + glyphosate fb glufosinate 7 DAIT was the only treatment reduced Palmer amaranth regrowth as compared to non-treated check. Results of this study suggested salvage treatment using auxin herbicide and glufosinate should be applied in sequence to be effective on large Palmer and should be only used when necessary due to variable efficacy observed in this study. Timely application to smaller weed (<10 cm) needs to be adhered to prevent large Palmer escapes in the first place as this weed grows rapidly under optimum conditions.