agronomy

Article Confirmation of Multiple Resistant radiata Population, Harvested in Colombian Rice Fields

Verónica Hoyos 1,* , Guido Plaza 2,* , José G. Vázquez-Garcia 3 , Candelario Palma-Bautista 3 , Antonia M. Rojano-Delgado 3 and Rafael De Prado 3

1 Facultad de Ingeniería, Universidad del Magdalena, Santa Marta, Magdalena 470004, Colombia 2 Departamento de Agronomía, Universidad Nacional de Colombia, Bogotá D.C. 111321, Colombia 3 Department of Agricultural Chemistry and Edaphology, University of Cordoba, 14071 Cordoba, Spain; [email protected] (J.G.V.-G.); [email protected] (C.P.-B.); [email protected] (A.M.R.-D.); [email protected] (R.D.P.) * Correspondence: [email protected] (V.H.); [email protected] (G.P.)

Abstract: This paper reports the first C. radiata population with resistance to glyphosate and multiple resistance to the acetolactate synthase (ALS) inhibitor, imazamox. Two populations, one putative resistant (R) and one susceptible (S), were used in the studies. Dose–response experiments were performed to evaluate the resistance factor (RF). Shikimic acid accumulation, 5-enolpyruvylshikimate- 3-phosphate synthase (EPSPS) and ALS enzyme activities were studied together with chemical integrated weed management (adjuvants and alternative herbicides). The resistance to glyphosate and imazamox was confirmed based on the dry weight reduction, visual evaluation and survival. The results of dose–response curve assays showed for the R population intermedium RF for glyphosate   (5.1 and 9.7 for amount of herbicide needed to reduce the dry weight by 50% GR50 and lethal dose of 50% LD50, respectively) and high RF for imazamox (34.9 and 37.4, respectively). The low shikimic Citation: Hoyos, V.; Plaza, G.; acid accumulation in R population confirmed the glyphosate resistance. The glyphosate concentration Vázquez-Garcia, J.G.; Palma-Bautista, C.; Rojano-Delgado, A.M.; De Prado, which inhibited the EPSPS enzyme in 50% (I50) was approximately 20 times higher for R population R. Confirmation of Multiple Resistant than the S population, while the imazamox I50 in ALS enzyme for the R was 89 times greater Chloris radiata Population, Harvested than the S plants. In the chemical integrated weed management, the foliar retention and effectivity in Colombian Rice Fields. Agronomy assays showed that the use of adjuvants improves the retention of glyphosate and imazamox, and 2021, 11, 496. https://doi.org/ the reduction in dry weight of weeds. The alternative herbicides study showed that the acetyl-CoA 10.3390/agronomy11030496 carboxylase (ACCase) inhibitors, paraquat and glufosinate, had better results for control in this species. However, poor control was observed with bispyribac-sodium, metsulfuron-methyl and Academic Editor: Connor Ferguson quinclorac, indicating possible cross-resistance for ALS-inhibitors and also multiple resistance for auxinic herbicides (quinclorac). Nevertheless dose–response experiments are required to confirm Received: 22 January 2021 this assumption. Accepted: 3 March 2021 Published: 6 March 2021 Keywords: glyphosate; ALS-inhibiting herbicides; imazamox; radiate fingergrass; chemical weed control

Publisher’s Note: MDPI stays neutral with regard to jurisdictional claims in published maps and institutional affil- 1. Introduction iations. Cultivated rice is among the most important cereal crops in the world, and plays an essential role in global food security and reduction in poverty [1,2]. For more than half of the world’s population, rice is a staple food, contributing 21% of their daily calorie

Copyright: © 2021 by the authors. intake [3]. For that reason, rice production has been described as the world’s single most Licensee MDPI, Basel, Switzerland. important economic activity [4]. In 2018, world rice production was highly localised. This article is an open access article Of the total paddy rice harvested area (167.1 million hectares), India was the primary distributed under the terms and producer with 27.6%, followed by China (18.2%). In America, ranks first as the conditions of the Creative Commons highest producer (30.4%), followed by the United States (19.3%), Colombia (10.4%) and Attribution (CC BY) license (https:// (7.1%) [5]. Rice is the fourth most important crop in Colombia after sugarcane, palm creativecommons.org/licenses/by/ oil and banana [6]. 4.0/).

Agronomy 2021, 11, 496. https://doi.org/10.3390/agronomy11030496 https://www.mdpi.com/journal/agronomy Agronomy 2021, 11, 496 2 of 14

In any rice production system, weeds are one of the main biological limitations, which cause yield reductions and affect the quality of paddy rice. Average losses worldwide are around 13%; however, rice cultivation in Colombia has reported losses from 30 to 73% due to weeds [7]. These losses vary depending on the floristic composition, community structure, sowing and tillage systems, water management, continuous planting of rice on the same piece of land, among other factors [8,9]. The most common weeds in rice crops around the world in the last 30 years are species of the Echinochloa genus (E. crus-galli and E. colona mainly) and weedy rice [2]. However, the most common weeds in rice crops in Colombia are Echinochloa colona (barnyardgrass), Oryza sativa (weedy rice), Cyperus iria, Ischaemum rugosum, Eleusine indica and Digitaria bicornis [10–12]. The genus Chloris as a weed is hardly known and includes numerous species dis- tributed in tropical and warm temperate regions [13]. Chloris radiata (L.) Sw. (basionym: Agrostis radiata L.), commonly known as radiate fingergrass, included in the family, is a C4, annual and native species in Colombia, growing between 500 and 2000 m above sea level [14]. It has been reported as a weed in rice crops since 2011, specifically in the central zone of the country, with no reports of yield losses in rice cultivation for this species. On the other hand, Chloris polydactyla reduces soybean growth by up to 70% due to competi- tion [15], Chloris truncata decreases wheat biomass and yield by 25% [16] and Chloris virgata causes yield losses in sorghum of about 37 thousand tons [17], showing the importance of the species of this genus and their impact on crops. Herbicides have become the most used weed control method worldwide. Currently, resistance to herbicides decreases the effectiveness and use of these products due to a lower level of control and the use of a single control method. [13]. Herbicides exert high selection pressure on weeds, and repeated and intensive use of them with the same mechanisms of action can complicate weed control and may hasten herbicide resistance evolution [18]. In Colombian rice crops, chemical control is frequently used and the applications are commonly carried out at different moments: pre-sowing, pre-emergence and postemergence (early–middle–late). In pre-sowing applications (before the establishment of the crop), an activity known as chemical-burning, non-selective active ingredients are usually used, and the objective is to reduce the density of weeds that could compete with the crop in its early stages of development [19]. The most commonly used herbicide is glyphosate with a frequency of use of 94% [20]. This active ingredient inhibits the enzyme 5-enolpyruvylshikimate-3- phosphate synthase (EPSPS), involved in the biosynthesis of the aromatic amino acids, phenylalanine, tyrosine and tryptophan in plants [21], which are essential as precursors for the production of hormones, cell wall formation and defence against pests [22]. In postemergence control, 100% of the farmers perform these applications using 23 different active ingredients [20]. The following active ingredients stand out for postemer- gence application in Colombian rice producing areas: propanil, bentazon, pyrazosulfuron, metsulfuron-methyl, carfentrazone, bispyribac-sodium, imazapic, imazamox, imazapyr, cyhalofop, fenoxaprop, profoxydim, 2,4-D, picloram and quinclorac [19]. The most frequent mechanism of action in this stage of application is acetolactate synthase (ALS) inhibitors, and about 50% of the farmers use them [20]. The primary mechanism of action of these herbicides is inhibition of branched chain amino acid synthesis [21]. In recent years, an increase in the distribution and density of C. radiata has been observed, attributable to possible failures of chemical control in rice crops, such as overuse of the same active ingredient or mode of action, overdose, monoculture, among others; suspecting that this weed has evolved resistance to herbicides. Therefore, the objectives of this research were: (1) to confirm glyphosate (EPSPS inhibitor) and imazamox (ALS inhibitor) resistance in one population; (2) to evaluate the resistance level of this popula- tion to both herbicides; and (3) study new chemical alternatives to control this resistant C. radiata population. Agronomy 2021, 11, 496 3 of 14

2. Materials and Methods 2.1. Chemicals Putative resistant (R) and known susceptible (S) Chloris radiata populations to glyphosate and imazamox, were sprayed with commercially formulated glyphosate and alternative herbicides (Table1). For the foliar retention and effectivity experiments, we used the following adjuvants: Retenol (66.5% terpenic alcohols w/v, DAYMSA, Zaragoza, Spain) and Trend® 90 (90% isodecyl ethoxylated alcohol w/v, FMC, Valencia, Spain). Retenol is a non-ionic adjuvant used to reduce the surface tension of droplets and thus, is intended to increase wettability, foliar retention and persistence of the active substances. Trend® 90 is a non-ionic wetting agent, which is used to improve the persistence and adherence of protection chemicals.

Table 1. Characteristics of commonly used herbicides to control this species (glyphosate and imazamox) and the alternatives herbicides used in “Integrated chemical management assay”.

Recommended Field Dose Herbicide HRAC/WSSA Code MOA Commercial Product (g ea-ai ha−1) b Glyphosate a 9 EPSPS Roundup Energy® (450 g/L SC) 960 Imazamox 2 ALS Pulsar® 40 (4% SC) 40 Bispyribac-sodium 2 ALS Bispyrifed® (100 SC) 50 Metsulfuron-methyl 2 ALS Ally® (60% WG) 9 Quizalofop-ethyl 1 ACCase Leopard (5% EC) 100 Clethodim 1 ACCase Select® (120 EC) 153 Quinclorac 4 Auxin Mimics Facet (25 SC) 375 Atrazine 5 PSII Gesaprim® (90% WDG) 2000 Glufosinate-ammonium 10 GS Finale® (15% p/v SL) 500 Oxyfluorfen 14 PPO Goal Supreme® (48%) 480 Paraquat 22 PSI Gramaxone® (27.6% SL) 400 Tembotrione 27 HPPD Laudis® (42% SC) 120 a g ea ha−1 = grams of equivalent acid per hectare. b g ai ha−1 = grams of active ingredient per hectare. HRAC: Herbicide-Resistance Action Committee; WSSA: Weed Science Society of America. MOA: Mode of action.

2.2. Plant Materials Seeds of Chloris radiata were collected in commercial rice fields from the Meseta zone of Ibague (4.376603◦, −75.149832◦), Central Zone in Colombia. This population was consid- ered to be resistant as the technicians and farmers of the area reported difficulty in chemical control with glyphosate and imazamox. The seeds of the susceptible population were collected in an area with no previous exposure to any herbicides (5.150360◦, −74.154028◦). Each population was defined as the mixture of seeds (bulk) collected in a single field. The seeds were sown in plastic pots (10 × 10 cm × 6.3 cm), filled with peat at field capacity and covered with parafilm. These pots were kept in a growth chamber (28/18 ◦C (day/night), 16-h photoperiod, 850 µmol m−2 s−1 light density and 60% relative humidity) until emergence (the plumule protruded). Seedlings were transplanted into 250 cm3 pots (1 plant per pot), filled with sand/peat (1:1 v/v). During the experiments, pots were placed in a greenhouse with controlled conditions (under 16-h day length with an average temperature of 28/20 ◦C day/night, relative humidity of 70–80%, typical conditions for rice growth in Colombia [23]) and were watered daily.

2.3. Fast Screening and Dose–Response Curve Assays Under controlled conditions, the herbicides, glyphosate and imazamox, were applied at the recommended rate (1X) to confirm the resistance occurrence in the collected C. radiata population (Table1). Herbicides were sprayed when plants reached the 3–4 leaf stage, using a laboratory chamber (De Vries Manufacturing, Hollandale, MN, USA), equipped with a TeeJet 8002 EVS flat fan nozzle calibrated to deliver 200 L ha−1 at 200 kPa at a height of 50 cm. The experiments were organised in a completely randomised design using ten plants (replicates) of each population per herbicide and dose (field dose and non-treated). This experiment was repeated twice. Twenty-eight days after treatment (DAT), visual evaluation of the percentage of control, survival and the reduction in dry Agronomy 2021, 11, 496 4 of 14

weight were analysed [24,25]. Visual evaluation (%) was based on the modified scale of Frans et al. [26], observing plant vigour and chlorosis compared with the untreated plants: 0% corresponded to no weed reduction or injury, 50% weed injury more lasting, recovery doubtful, and 100% when the herbicide had a total effect on the plants. For the dose–response curve experiments, the herbicides were applied on the same populations at the same leaf stage (3–4 fully extended leaves). For glyphosate, treatments were performed using the following doses: 0, 31.25, 62.50, 125, 250, 500, 1000, 2000, 3000 and 4000 g ae ha−1. For imazamox, the following doses were used: 0, 0.65, 1.25, 2.5, 5, 10, 20, 30, 40, 80, 160, 320, 640 and 1080 g ai ha−1. The treatments were applied in the laboratory chamber under the same application conditions mentioned above. The experiment was arranged in a completely randomised design using ten plants of each population per herbicide and dose. This experiment was repeated twice.

2.4. Shikimic Accumulation Assay For this experiment, the methodology described by Fernández-Moreno et al. [27] was followed. Samples (50 mg) of leaf segments were harvested from the youngest fully expanded leaf from a pool of 20 plants per population at the 3–4 leaf stage. The glyphosate concentrations used were: 0, 100, 250, 500 and 1000 µM. The samples were measured in a spectrophotometer at 380 nm within 30 min. The assay was repeated twice with three replicates per glyphosate concentration for each population. The results were expressed as mg shikimic acid g−1 fresh weight.

2.5. EPSPS Enzyme Activity For this assay the methodology described by Vázquez-García et al. [13] was followed. Approximately 5 g of leaf tissue were powdered using liquid nitrogen. The EPSPS activity was determined using EnzChek Phosphate Analysis Kit (Invitrogen, Carlsbad, CA, USA). The substrates for the EPSPS enzyme reaction were phosphoenolpyruvate (1.02 mM) and shikimate-3-phosphate (0.41 mM), supplied by Sigma-Aldrich (Madrid, Spain). Different glyphosate concentrations (0, 0.1, 1, 10, 100, and 1000 µM) were used to determine the inhibition of enzymatic activity (I50). The used assay buffer was composed of 1 mM MgCl2, 10% glycerol, 100 mM MOPS, 2 mM sodium molybdate and 200 mM NaF. EPSPS activity was measured at 360 nm in a spectrophotometer (DU-640, Beckman Coulter Inc. Fullerton, CA, USA) to determine the amount of inorganic phosphate (µmol) released, measured in µg−1 TSP min−1. The total content of protein in crude extract was measured at 595 nm with the Bradford colorimetric method [28]. Three replicates per population and glyphosate concentration were used, and the experiment was repeated twice.

2.6. ALS Enzyme Activity ALS enzyme activity was measured as described Hatami et al. [29]. For this, 3 g of young foliar tissue (from the 4–5 leaves stage) was cut, frozen in liquid nitrogen and powdered with the addition of PVPP. The supernatant obtained in the extraction step was immediately used for ALS enzyme activity assays. ALS activity was assayed by adding 0.05 mL of enzyme extract to 0.1 mL of freshly prepared assay buffer (0.08 M potassium phosphate, pH 7.5, 0.15 M sodium pyruvate, 1.5 mM MgCl2, 1000 µM FAD) and increasing concentrations of technical-grade imazamox. After mixture incubation (37 ◦C for 1 h), the reaction was stopped by the addition of ◦ 0.05 mL of H2SO4 (3 M). The reaction tubes were then heated (15 min at 60 C) to facilitate decarboxylation of acetolactate to acetoin. Acetoin was detected as a coloured complex (520 nm) formed after the addition of 0.25 mL of creatine (5 g L−1, freshly prepared in water) and 0.25 mL of α-naphthol (50 g L−1, freshly prepared in 5 M NaOH) and incubated (60 ◦C for 15 min). The background was determined using control vials, in which the reaction was stopped before incubation and measured. Maximum ALS specific activity (nmol of acetoin mg−1 of protein h−1) was determined in the absence of herbicide and expressed as 100%. Total protein content was measured using the Bradford method [28]. Three Agronomy 2021, 11, 496 5 of 14

replicates per population and imazamox concentration were used, and the experiment was repeated twice.

2.7. Chemical Integrated Management 2.7.1. Effectivity with and without Adjuvants Under greenhouse conditions, an experiment was carried out to evaluate the dry weight reduction (%) of the weed at 28 DAT. For this experiment the dose used for the her- bicides was selected according to the dose of the herbicide that causes a growth reduction equivalent to 50% (GR50); in the R population the dose of glyphosate was 485 g ae h−1, and 150 g ai h−1 for imazamox; in the S population the doses used were 95 g ae h−1 and 4.5 g ia h−1, respectively. The plants were sprayed with and without adjuvants (Trend® 90 at 2 mL L−1 and Retenol® at 4 mL L−1). Herbicide applications were made using the same equipment described above at the 3–6 leaf stage. The experiment was repeated twice with 10 replicates per dose of adjuvants and herbicide.

2.7.2. Foliar Retention with and without Adjuvants The methodology described by Domínguez-Mendez et al. [30] was followed for this experiment. In the foliar retention assays, a solution of glyphosate (360 g ae ha−1) and of imazamox (40 g ai ha−1) with and without adjuvant (same doses as in effectivity assay) were applied to six plants (replicates) with four leaves, adding a visual indicator (100 mg of fluorescein per litre of 5 mM NaOH). The treatments were applied in the laboratory chamber mentioned in fast screening and dose–response curve assays under the same application conditions. After one hour, once the leaves were dried, the plants were cut at soil level and placed individually in test tubes covered with paraffin paper, containing 50 mL of 5 mM NaOH each. Subsequently, this was vigorously shaken for 30 s to eliminate possible residues of herbicide and dye that could remain on the leaf tissue. In a spectrofluorimeter (F-2500, Hitachi, Tokyo, Japan), the readings of the wash solutions were made, at a wavelength of 490 nm for excitation and 510 nm for emission. Finally, the cut tissues were packed into paper bags and dried in an oven at 80 ◦C for 72 h for later weighing. The retention was expressed in µL of herbicide per g of dry matter. This experiment was repeated twice.

2.7.3. Alternative Herbicide Greenhouse experiments were performed in R and S populations of C. radiata, testing ten herbicides with eight different mechanisms of action at the recommended field dose (Table1). At visual evaluation higher than 80% the control was considered satisfactory, at between 50 and 75% it was considered intermediate and unsatisfactory at less than 50% [26]. Using the same laboratory chamber and calibration mentioned in the dose–response assay, each herbicide was sprayed on ten (replicates) young (3–4 true leaf stage) plants in a completely randomised design, and the experiment was repeated twice. Ten plants were used as a control for all treatments. At 28 DAT, visual evaluation (%), survival (%) and dry weight reduction were measured for each treatment.

2.8. Statistical Analysis Non-linear regression analysis was conducted to determine the amount of herbicide needed to reduce the dry weight by 50% (GR50), lethal dose of 50% (LD50) and the herbicide concentration causing 50% inhibition of enzyme activity (I50) of each C. radiata population. The log-logistic model with three parameters to inhibit shoot growth, lethal dose and enzyme activity was conducted, under the following equation (Equation (1)):

d − c Y = c + (1) 1 + exp(b(log(x) − log(e)))

Model Y represents the growth response (dry weight, survival or enzyme activity) to dose x of the herbicide; d is the upper limit of the curve; c is the lower limit (fixed at 0); Agronomy 2021, 11, 496 6 of 14

b is the slope at the inflection point (i.e., GR50, LD50 or I50); x is the herbicide dose; e the herbicide concentration required to inhibit shoot growth, lethal dose and enzyme activity by 50% [31,32]. The resistance factors (RF = R/S). were computed as R-to-S GR50, LD50, or I50 ratios. Statistical analysis was carried out with R version 4.0.4 [33] (Vienna, Austria) and its dose–response curves extension package drc and lmtest [34]. An analysis of variance (ANOVA) was conducted on data for shikimic acid, foliar retention, effectivity using adjuvants and alternative herbicides. For the statistical analysis, model assumptions of normal distribution of errors and homogeneous variance were graph- ically inspected, data were tested for Shapiro–Wilk normality and Hartley homoscedasticity. Significant differences were compared using Tukey’s test at the 95% probability level. The ANOVAs were performed using Statistix software (version 10.0) from Analytical Software (Tallahassee, FL, USA). To jointly analyse the data of experiments repeated twice, an analy- sis of variance was performed, considering each run as a random factor. To prove above, an analysis of residual homogeneity between runs was performed, dividing the largest sum of squares by the smallest, all the results were lesser than seven thus it was considered homogeneity to mix both runs.

3. Results 3.1. Fast Screening and Dose–Response Curve Assays The fast-screening assay at commercial doses showed that the S population was con- trolled by glyphosate and imazamox (Table2). For the R population, both herbicides showed dry weight reduction compared to untreated plants higher than 60%, visual evalu- ation less than 70% and a survival of 100% (Table2), confirming resistance to glyphosate and imazamox in this species.

Table 2. Effect of glyphosate and imazamox, and the alternatives herbicides used in “Integrated chemical management assay” in Chloris radiata. Percentage of visual evaluation, survival and dry weight (DW) reduction compared to the untreated controls in the resistant (R) and susceptible (S) populations.

Visual Evaluation (%) a Survival (%) b DW Reduction (%) Herbicide SRSRSR Glyphosate 100 ± 0 50.1 ± 9.2 0 100 ± 0 96.0 ± 3.3 A 70.8 ± 8.1 B Imazamox 92 ± 7 66.0 ± 9.4 10.3 ± 5 100 ± 0 94.6 ± 3.8 A 69.0 ± 5.9 B Bispyribac-sodium 100 ± 0 30.3 ± 8.6 0 100 ± 0 100 ± 0 A 18.5 ± 8.1 C Metsulfuron-methyl 100 ± 0 30.0 ± 5.6 0 100 ± 0 100 ± 0 A 13.2 ± 8.5 C Quizalofop-ethyl 100 ± 0 100 ± 0 0 0 100 ± 0 A 100 ± 0 A Clethodim 100 ± 0 100 ± 0 0 0 100 ± 0 A 100 ± 0 A Quinclorac 100 ± 0 19.9 ± 7.3 0 100 ± 0 100 ± 0 A 16.1 ± 8.4 C Atrazine 100 ± 0 100 ± 0 20.0 ± 6.5 20.1 ± 5.5 81.9 ± 8.4 B 83.2 ± 9.1 B Glufosinate-ammonium 100 ± 0 100 ± 0 0 0 100 ± 0 A 100 ± 0 A Oxyfluorfen 100 ± 0 100 ± 0 10.0 ± 4 10.1 ± 3 85.2 ± 6.8 B 84.6 ± 9.4 B Paraquat 100 ± 0 100 ± 0 0 0 100 ± 0 A 100 ± 0 A Tembotrione 100 ± 0 100 ± 0 0 0 100 ± 0 A 100 ± 0 A a The visual evaluation was based in the modified scale of Frans et al. (1986). b Survival was evaluated by the ability of the plant to produce new leaves and/or have active growth. The means with different letters within a column and for each herbicide are significantly different with a 95% probability determined by Tukey’s test: n = 10.

The glyphosate dose to reduce the dry weight (GR50) and to permit a survival −1 (LD50) by 50% of the R biotype were 481.53 ± 64.06 and 4242.39 ± 561.72 g ae ha , respectively, with a RF of 5.1 and 9.68 for these parameters. For imazamox the resis- tant population needed 34.89-fold the dose of the S to decrease the dry weight by 50% −1 (GR50 = 155.45 ± 7.9 g ai ha ) and based on LD50 values it was 37-fold more resistant (Figure1, Table3). Agronomy 2021, 11, x 7 of 15

Paraquat 100 ± 0 100 ± 0 0 0 100 ± 0 A 100 ± 0 A Tembotrione 100 ± 0 100 ± 0 0 0 100 ± 0 A 100 ± 0 A a The visual evaluation was based in the modified scale of Frans et al. (1986). b Survival was evaluated by the ability of the plant to produce new leaves and/or have active growth. The means with different letters within a column and for each herbicide are significantly different with a 95% probability determined by Tukey’s test: n = 10.

The glyphosate dose to reduce the dry weight (GR50) and to permit a survival (LD50) by 50% of the R biotype were 481.53 ± 64.06 and 4242.39 ± 561.72 g ae ha−1, respectively, Agronomy 2021, 11, 496 with a RF of 5.1 and 9.68 for these parameters. For imazamox the resistant population7 of 14 needed 34.89‐fold the dose of the S to decrease the dry weight by 50% (GR50 = 155.45 ± 7.9 g ai ha−1) and based on LD50 values it was 37‐fold more resistant (Figure 1, Table 3).

FigureFigure 1. Effects 1. Effects of theof the glyphosate glyphosate and and imazamox imazamox dose on the the dry dry weight weight reduction reduction (A (,BA), Band) and plant plant survival survival (C,D ()C of,D the) of the untreateduntreated (control) (control)Chloris Chloris radiata radiataS( S (○)) and and R R ((∆∆) populations, expressed expressed as as a percentage a percentage of the of the mean mean (n = ( 10)n = ± 10) SE.± SE. # Table 3. Parameters of the log‐logistic equation used to calculate the herbicide dose required for a 50% reduction in dry Table 3. Parameters of the log-logistic equation used to calculate the herbicide dose required for a 50% reduction in dry weight (GR50) and lethal dose (LD50). weight (GR50) and lethal dose (LD50). Herbicide C. radiata d b p‐Value GR50/LD50 RF c Herbicide C. radiata d b p-Value GR /LD RF c GR50 value 50 50 S 99.13 1.45 GR< 2.2value × 10−16 95.15 ± 13.59 a 50 Glyphosate −16 a S R 99.13100.25 1.451.48 < <2.22.2 ×× 1010−16 481.5395.15 ± 64.06± 13.59 5.06 (5.01–5.09) Glyphosate −16 R S 100.25102.26 1.482.26 <2.20.9998× 10 4.45481.53 ± 0.3± 64.06 5.06 (5.01–5.09) Imazamox b ± b S R 102.26100.64 2.263.83 0.9999 0.9998 155.45 4.45 ± 7.90.3 34.90 (34.40–35.60) Imazamox R 100.64 3.83 0.9999 155.45 ± 7.9 34.90 (34.40–35.60)

LD50 value S 100.05 10.57 <2.2 × 10−16 438.18 ± 91.21 Glyphosate R 100.04 4.87 <2.2 × 10−16 4242.39 ± 561.72 9.70 (9.10–10.60) S 102.65 1.31 <2.2 × 10−16 4.65 ± 0.27 Imazamox 37.43 (37.31–37.56) R 100.62 2.26 <2.2 × 10−16 174.06 ± 9.51 a −1 b −1 c g ae ha , g ai ha , RF (resistance factor) = GR50,R/GR50,S or LD50,R/LD50,S; (numbers in parentheses are the confidence interval).

3.2. Shikimate Accumulation As the dose of glyphosate was increased, the accumulation of shikimic acid gradually increased in both populations (R and S) of C. radiata, but the susceptible populations showed higher accumulation compared with resistant ones. For the S population, 43.5% more shikimic acid accumulates at the highest glyphosate concentration evaluated compared to the lowest concentration. For the R population the difference was 13%. At the lowest Agronomy 2021, 11, x 8 of 15

LD50 value S 100.05 10.57 <2.2 × 10−16 438.18 ± 91.21 Glyphosate R 100.04 4.87 < 2.2 × 10−16 4242.39 ± 561.72 9.70 (9.10–10.60) S 102.65 1.31 < 2.2 × 10−16 4.65 ± 0.27 Imazamox 37.43 (37.31–37.56) R 100.62 2.26 < 2.2 × 10−16 174.06 ± 9.51 a g ae ha−1, b g ai ha−1, c RF (resistance factor) = GR50,R/GR50,S or LD50,R/LD50.S; (numbers in parentheses are the confidence interval).

3.2. Shikimate Accumulation As the dose of glyphosate was increased, the accumulation of shikimic acid gradually increased in both populations (R and S) of C. radiata, but the susceptible populations showed higher accumulation compared with resistant ones. For the S population, 43.5% more shikimic acid accumulates at the highest glyphosate concentration evaluated com‐ Agronomy 2021, 11, 496 pared to the lowest concentration. For the R population the difference8 of 14 was 13%. At the lowest concentration of glyphosate (250 μM), S plants accumulated 2.5 times more shi‐ kimic acid than R plants, and at the highest concentration (2000 μM) the difference was concentration of glyphosate (250 µM), S plants accumulated 2.5 times more shikimic acid −1 3.1than times R plants, greater and at(∼ the2.1 highest ± 0.16 concentration mg shikimic (2000 acidµM) g the fresh difference weight) was 3.1 than times the R population (Figuregreater ( 2).∼2.1 ± 0.16 mg shikimic acid g−1 fresh weight) than the R population (Figure2).

2.50 a a

fresh 2.00 a a −1 1.50

1.00 b R b b b weight) 0.50 S

0.00

Shikimic acid (mg g 250 500 1000 2000 Glyphosate concentration (µM)

Figure 2. Shikimic acid accumulation of glyphosate-susceptible and -resistant Chloris radiata plants Figureat different 2. Shikimic glyphosate acid concentrations. accumulation Vertical of bars glyphosate represent the‐susceptible standard error and of ‐ theresistant mean (n =Chloris 3 radiata plants attechnical different replicates). glyphosate Means concentrations. with different letters Vertical within are bars statistically represent different the atstandard 95% probability error of the mean (n = 3 technicaldetermined replicates). by the Tukey Means test. with different letters within are statistically different at 95% probabil‐ ity3.3. determined EPSPS Enzyme by Activitythe Tukey test.

The I50 (glyphosate concentration to reduce the enzyme activity by 50%) in the S Agronomy 2021, 11, x 3.3.population EPSPS was Enzyme 0.22 µM, Activity while for the R population was 4.36 µM. These results showed9 of the 15 activity of the enzyme in the R population was approximately 20 times higher compared to The I50 (glyphosate concentration to reduce the enzyme activity by 50%) in the S pop‐ the S population (Figure3A). ulation was 0.22 μM, while for the R population was 4.36 μM. These results showed the activity of the enzyme in the R population was approximately 20 times higher compared to the S population (Figure 3A).

Figure 3. (A) EPSPS and (B) ALS enzyme activity expressed as a percentage of the untreated control in leaf extracts of Figure 3. (A) EPSPS and (B) ALS enzyme activity expressed as a percentage of the untreated control in leaf extracts of glyphosate/imazamox‐susceptible and ‐resistant Chloris radiata plants. glyphosate/imazamox-susceptible and -resistant Chloris radiata plants. 3.4. ALS Enzyme Activity

3.4. ALSThe Enzymeimazamox Activity concentration needed to inhibit the ALS activity by 50% (I50) in the S

populationThe imazamox was 5.47 μ concentrationM, while that needed in the toR population inhibit the ALSwas activity487 μM, by which 50% means (I50) in the the R S population was was approximately 5.47 µM, while 89 that‐fold in themore R resistant population to imazamox was 487 µM, than which the S means population the R (Figurepopulation 3B). was approximately 89-fold more resistant to imazamox than the S population (Figure3B). 3.5. Integrated Chemical Management 3.5.1. Effectivity with and without Adjuvants The results of the effectivity experiment were similar to those of foliar retention, showing the effect of the addition of adjuvants in better control of susceptible and resistant populations of C. radiata. For glyphosate and imazamox resistant populations, the use of Trend® 90 adjuvant showed the best results, increasing the dry weight reduction by 50% for glyphosate and 32% for imazamox (Table 4).

Table 4. Dry weight reduction (%) and increased effectiveness (%) with glyphosate and imazamox in the presence and absence of adjuvants from the R and S populations of Chloris radiata.

Glyphosate Treatment S (95 g ae ha−1) % IE a R (485 g ae ha−1) % IE a Only Herbicide 51.30 ± 3.82 B ‐ 54.82 ± 3.83 C ‐ Herbicide + Retenol 65.68 ± 3.64 A 28.03 (25.76–30.66) 71.36 ± 3.98 B 30.17 (28.45–32.14) Herbicide + Trend 90 70.82 ± 2.11 A 38.05 (32.31–44.71) 81.98 ± 2.11 A 49.54 (43.37–56.63) Imazamox S (4.5 g ai ha−1) % IE a R (150 g ai ha−1) % IE a Only Herbicide 52.06 ± 2.70 B ‐ 48.72 ± 2.42 B ‐ Herbicide + Retenol 60.22 ± 4.18 A 15.67 (13.53–17.60) 58.06 ± 3.85 A 19.17 (17.08–21.05) Herbicide + Trend 90 63.20 ± 3.58 A 21.39 (20.78–21.95) 64.62 ± 4.08 A 32.63 (30.75–34.33) a IE = Increase effectiveness in the control (%) [35]; (numbers in parentheses are the confidence). The means with different letters within a column and for each herbicide are significantly different with a 95% probability determined by Tukey’s test: n = 10.

3.5.2. Foliar Retention with and without Adjuvants The use of adjuvants increased herbicide retention for both R and S populations of C. radiata. The increase in foliar retention was higher for glyphosate than imazamox, regard‐ less of the population. For glyphosate, the addition of Trend® 90 showed the best results with increases in retained herbicide higher than 250% in the R and S populations (Table

Agronomy 2021, 11, 496 9 of 14

3.5. Integrated Chemical Management 3.5.1. Effectivity with and without Adjuvants The results of the effectivity experiment were similar to those of foliar retention, showing the effect of the addition of adjuvants in better control of susceptible and resistant populations of C. radiata. For glyphosate and imazamox resistant populations, the use of Trend® 90 adjuvant showed the best results, increasing the dry weight reduction by 50% for glyphosate and 32% for imazamox (Table4).

Table 4. Dry weight reduction (%) and increased effectiveness (%) with glyphosate and imazamox in the presence and absence of adjuvants from the R and S populations of Chloris radiata.

Glyphosate Treatment S (95 g ae ha−1) % IE a R (485 g ae ha−1) % IE a Only Herbicide 51.30 ± 3.82 B - 54.82 ± 3.83 C - Herbicide + Retenol 65.68 ± 3.64 A 28.03 (25.76–30.66) 71.36 ± 3.98 B 30.17 (28.45–32.14) Herbicide + Trend 90 70.82 ± 2.11 A 38.05 (32.31–44.71) 81.98 ± 2.11 A 49.54 (43.37–56.63) Imazamox S (4.5 g ai ha−1) % IE a R (150 g ai ha−1) % IE a Only Herbicide 52.06 ± 2.70 B - 48.72 ± 2.42 B - Herbicide + Retenol 60.22 ± 4.18 A 15.67 (13.53–17.60) 58.06 ± 3.85 A 19.17 (17.08–21.05) Herbicide + Trend 90 63.20 ± 3.58 A 21.39 (20.78–21.95) 64.62 ± 4.08 A 32.63 (30.75–34.33) a IE = Increase effectiveness in the control (%) [35]; (numbers in parentheses are the confidence). The means with different letters within a column and for each herbicide are significantly different with a 95% probability determined by Tukey’s test: n = 10.

3.5.2. Foliar Retention with and without Adjuvants The use of adjuvants increased herbicide retention for both R and S populations of C. radiata. The increase in foliar retention was higher for glyphosate than imazamox, regardless of the population. For glyphosate, the addition of Trend® 90 showed the best results with increases in retained herbicide higher than 250% in the R and S populations (Table5). Moreover, this adjuvant also presented the best result for imazamox; nevertheless, the R plants had greater retained herbicide (205%) than the S plants (154%) (Table5).

Table 5. Foliar retention (expressed as g−1 dry matter) of glyphosate (360 g ae ha−1) and imazamox (40 g ai ha−1) with and without adjuvants and increased retained herbicide in R and S populations of Chloris radiata.

Glyphosate Treatment S R % IRH a % IRH a (µL g−1 dry Matter) (µL g−1 dry Matter) Only Herbicide 377.68 ± 10.11 C - 335,18 ± 17.37 C - Herbicide + Retenol 1146.69 ± 49.95 B 203.61 (198.37–208.57) 1034.69 ± 24.30 B 208.69 (200.38–217.92) Herbicide + Trend 90 1390.17 ± 31.94 A 268.08 (266.72–269.51) 1186.96 ± 46.23 A 254.12 (249.79–258.93) Imazamox S R % IRH a % IRH a (µL g−1 dry Matter) (µL g−1 dry Matter) Only Herbicide 153.91 ± 17.22 C - 121.07 ± 12.46 C - Herbicide + Retenol 321.60 ± 12.91 B 108.95 (95.47–125.83) 291.71 ± 19.74 B 140.94 (133.24–150.40) Herbicide + Trend 90 390.67 ± 16.91 A 153.83 (138.16–173.43) 370.39 ± 12.50 A 205.93 (186.74–229.51) a IRH = Increased retained herbicide (%) [35]; (numbers in parentheses are the confidence). The means with different letters within the R and S columns and for each herbicide are significantly different from the 95% probability determined by Tukey’s test: n = 6.

3.5.3. Alternative Herbicides Almost all herbicides used in the postemergence weed treatments were effective for control of resistant population, with values of 100% on visual evaluation, with the exception of bispyribac-sodium, metsulfuron-methyl and quinclorac. For these herbicides, the control was unsatisfactory and there was no decrease in plant growth compared with Agronomy 2021, 11, 496 10 of 14

the susceptible population (Table2). The survival percentage and the dry weight reduction showed the same.

4. Discussion The Chloris genus presents a certain level of natural tolerance to glyphosate, evidenced in the differential response of some species [36–38]. Nonetheless, the results of the present study confirm the first case of Chloris radiata with glyphosate and imazamox resistance. Glyphosate resistance has been studied in other species of the same genus, such as C. polydactyla, C. elata, C. virgata, C. truncata, C. barbata and more recently in C. disti- chophylla [13,36–39]. The resistance factor based on GR50 obtained in this study (RF = 5.1) is similar to Brazilian research for C. distichophylla (RF = 5.1) [13] and C. elata (RF = 5.4) [39], and in Mexico for C. barbata (RF = 4.8) [38]. However, the glyphosate dose required to con- trol a plant population by 50% (LD50) is higher than that reported in the studies mentioned above but similar to studies conducted in Australia [40,41]. This active ingredient is used in rice crops in Colombia mainly in pre-sowing and can also be used in pre-emergent crop applications, to control weedy rice and other weeds considered difficult to control [19]. The low accumulation of shikimic acid in resistant populations (3.1 times less) com- pared to susceptible populations evidences the loss of susceptibility to glyphosate (Figure2 ). Similar results were reported in C. elata from and Brazil (4.9 and 5.4 times, respec- tively) [37,39], C. truncata (2.4–8.7) and C. virgata (2.0–9.7) from Australia [40,41]. Accumu- lation differences between susceptible and resistant populations are a rapid and reliable indicator of glyphosate resistance [42]. Despite that, this parameter is only an indicator of resistance and indicates a limited interaction between the herbicide and the EPSPS protein [38]. For the genus Chloris, the current study is the first report of imazamox resistance. C. radiata showed high resistance factors based on GR50 and LD50 (34.89 and 37.43, respec- tively). These results differ from those obtained in studies in Echinochloa colona (2.5), Lolium perenne ssp. multiflorum (5.3 and 17.48), and Bromus tectorum (110) [43–45]. Imazamox is used in Clearfield production systems [19], which started to be used in Colombia in 2003 [46]. Currently, there is only one report of resistance to imidazolinones in Colombia; weedy rice resistant to imazapyr and imazamox [47]. The confirmation of imazamox resistance is demonstrated by I50 for R plants, which was 89 times greater than S plants. This result shows the important role that the enzyme plays in resistance to imazamox [48]. Broadly and based on ALS enzyme inhibition by ALS inhibitors, a high level of resistance indicates the presence of simple or multiple mutations in the ALS enzyme of resistant plants [49]. It is not only mutations that can be the mechanisms in the target site, it also can be due to an increase in the ALS gene copy number and amplification [50]. Based on chemical integrated management of resistant population of C. radiata to glyphosate and imazamox, it was evident that the use of adjuvants improved the control of the species for both herbicides. One of the factors to improve the efficacy of herbicides is increasing the absorption into plant foliage, and the use of adjuvants is an important tool for this [51]. Laboratory experiments (foliar retention) showed increases greater than 200% in the effectiveness of the active ingredients, where the use of Trend® 90 presented the best results. Palma-Bautista et al. [35] found similar results when they added adju- vants to glyphosate applications for control of resistant L. rigidum and Conyza canadiensis populations. In greenhouse experiments, the effectiveness test did not show increases as significant as the previous test; nevertheless, it increased the effectiveness with the use of adjuvants by 40% for glyphosate and 25% for imazamox; again Trend® 90 presented the best results. Trend® 90 is a non-ionic surfactant, this kind of adjuvant is the most commonly used in agriculture and its main characteristic is breaking water surface tension which allows a better covering and penetration [51]. In the alternative herbicide test for control of resistant C. radiata populations, poor weed control was achieved using both bispyribac-sodium and metsulfuron-methyl, indicat- Agronomy 2021, 11, 496 11 of 14

ing a possible cross-resistance for other ALS inhibitors. Similarly, low control percentages (<20%) were recorded using auxinic herbicides, showing possible multiple resistance with quinclorac; both cases still await verification. In Colombia, there are some reports of resis- tance to these active ingredients in Murdannia nudiflora, Ischaemum rugosum and E. colona, also in rice fields [25,52,53]. Initially, when bispyribac-sodium was introduced, the control of different weeds was satisfactory, and farmers preferred using this herbicide than other alternatives due to its crop selectivity, low dosage, high efficiency and versatility, which led to more than 90% of the area being treated with this active ingredient [53]. Quinclorac, a quinolinecarboxylic acid, has 11 reports of resistance, of which ten are associated with rice cultivation [47], due to its selectivity to cultivation and good control of species of the Echinochloa complex [54]. For example, in the central rice zone in Colombia, 54% of the area routinely used quinclorac mainly in late postemergence for control of E. colona [25]. Weed management implemented in Colombian rice showed high dependence on chemical con- trol, including the use of quinclorac, propanil, fenoxaprop-ethyl, profoxydim, sulfonylurea and bispyribac-sodium [53]. The alternative herbicides evaluated are viable tools to prevent the spread of this species, especially ACCase-inhibiting graminicide herbicides in postemergence applica- tions, and paraquat and glufosinate in pre-sowing applications. Similar results were reported in C. distichophylla from Brazil, where herbicides such as clethodim, quizalofop, paraquat and glufosinate showed total control of the plants [13]; meanwhile paraquat, glu- fosinate and atrazine have high control in the early stages of the weed [55], and setoxydim and haloxyfop-p-methyl have control higher than 90% [56]. Recent studies on glyphosate- resistant C. virgata and C. truncata with sequential herbicide applications, showed that the best control was haloxyfop-paraquat treatment with a few days (1–4) between ap- plications, and glyphosate-paraquat only for C. truncata [57]. Other research has shown that isoxaflutole, haloxyfop and different photosystem II inhibitors (atrazine, simazine, terbuthylazine) in a tank mixture with paraquat were effective in controlling C. virgata [58]. The best strategies for managing herbicide-resistant weeds are in diversification, seeking to reduce selection pressure and to control resistant populations. Our results demonstrate that including different mechanisms of action in integrated weed management is a good al- ternative. However, farmers should diversify all weed control practices, including rotation in cropping systems [59].

5. Conclusions Chloris radiata is a species that has become a problem in recent years, attributable to possible failures in chemical control. Our research confirms the first case of glyphosate resistance and multiple resistance to ALS inhibitor (imazamox), with intermedium resistant factor for glyphosate and high for imazamox. The results of alternative herbicide experi- ments evidenced a possible cross-resistance (bispyribac-sodium and metsulfuron-methyl) and another multiple resistance (quinclorac) resulting in poor control of the species. New studies to confirm these resistances and elucidate resistance mechanisms are being con- ducted. Based on integrated chemical management, we concluded that the use of adjuvants improved foliar retention and effectivity of glyphosate and imazamox. On the other hand, the ACCase-inhibitor herbicides, paraquat and glufosinate, showed better results for the control of resistant C. radiata.

Author Contributions: Conceptualization, V.H., G.P., J.G.V.-G., C.P.-B., A.M.R.-D., and R.D.P.Method- ology, V.H., G.P. and J.G.V.-G. Validation, V.H., G.P., J.G.V.-G., C.P.-B., A.M.R.-D., and R.D.P. Formal analysis, V.H., J.G.V.-G., C.P.-B. and A.M.R.-D. Investigation, V.H., G.P., J.G.V.-G., C.P.-B., A.M.R.-D., and R.D.P. Resources, R.D.P. Data curation, V.H. and J.G.V.-G. Writing—original draft preparation, writing—review and editing, visualization, V.H., G.P., J.G.V.-G., C.P.-B., A.M.R.-D., and R.D.P. Super- vision, project administration, funding acquisition, V.H., G.P. and R.D.P. All authors have read and agreed to the published version of the manuscript. Funding: This research was funded by Universidad del Magdalena, Universidad Nacional de Colombia and Asociación de Agroquímicos y Medioambiente (Cordoba, Spain). Agronomy 2021, 11, 496 12 of 14

Institutional Review Board Statement: Not applicable. Informed Consent Statement: Not applicable. Data Availability Statement: The raw data will be made available as requested. Acknowledgments: Special thanks to Fedearroz staff for their help in obtaining the populations, Alejandra Díaz and David Mora-García for help with greenhouse experiments. Conflicts of Interest: The authors declare no conflict of interest.

Abbreviations ALS: acetolactate synthase; EPSPS: 5-enolpyruvylshikimate-3-phosphate synthase; ACCase: acetyl- CoA carboxylase; R: resistant population; S: susceptible population; RF: resistance factor; GR50: dose of herbicide needed to reduce the fresh weight by 50%; LD50: lethal dose of 50%. I50: herbicide concentration causing 50% inhibition of enzyme activity; g ea ha−1 = grams of equivalent acid per hectare; g ai ha−1 = grams of active ingredient per hectare; HRAC: Herbicide-Resistance Action Com- mittee; WSSA: Weed Science Society of America; MOA: Mode of action; DAT: days after treatment; DW: dry weight; IE = Increase effectiveness in the control; IRH = Increased retained herbicide.

References 1. Prasad, R.; Shivay, Y.S.; Kumar, D. Current Status, Challenges, and Opportunities in Rice Production. In Rice Production Worldwide; Chauhan, B.S., Jabran, K., Mahajan, G., Eds.; Springer International Publishing AG: Cham, Switzerland, 2017; pp. 1–32. 2. Singh, V.; Zhou, S.; Ganie, Z.; Valverde, B.; Avila, L.; Marchesan, E.; Merotto, A.; Zorrilla, G.; Burgos, N.; Norsworthy, J.; et al. Rice Production in the Americas. In Rice Production Worldwide; Chauhan, B.S., Jabran, K., Mahajan, G., Eds.; Springer International Publishing AG: Cham, Switzerland, 2017; p. 168. 3. Awika, J.M. Major Cereal Grains Production and Use around the World. In Advances in Cereal Science: Implications to Food Processing and Health Promotion; Awika, J.M., Piironen, V., Bean, S., Eds.; American Chemical Society ACS Symposium Series: Washington, DC, USA, 2011; pp. 1–13. 4. Ziska, L.H.; Gealy, D.R.; Burgos, N.; Caicedo, A.L.; Gressel, J.; Lawton-Rauh, A.L.; Avila, L.A.; Theisen, G.; Norsworthy, J.; Ferrero, A.; et al. Weed (Red) Rice: An Emerging Constraint to Global Rice Production. In Advances in Agronomy 129; Sparks, D.L., Ed.; Academic Press: Cambridge, MA, USA, 2015; pp. 181–228. 5. FAOSTAT. FAO Statistical Databases. Available online: http://www.fao.org/faostat/en/#data/QC (accessed on 8 August 2020). 6. Hoyos, V.; Plaza, G.; Li, X.; Caicedo, A.L. Something Old, Something New: Evolution of Colombian Weedy Rice (Oryza Spp.) through de Novo de-Domestication, Exotic Gene Flow, and Hybridization. Evol. Appl. 2020, 13, 1968–1983. [CrossRef][PubMed] 7. Cobb, A.H.; Reade, J.P.H. Herbicides and Plant Physiology; Wiley-Blackwell: Oxford, UK, 2010. 8. Fuentes, C. Manejo de Las Malezas Del Arroz En América Latina: Problemas y Soluciones. In Produccion Eco-Eficiente del Arroz en América Latina; Degiovanni, B.V., Martinez, R.C.P., Motta, O.F., Eds.; Centro Internacional de Agricultura Tropical: Cali, Colombia, 2010; pp. 391–412. 9. Fahad, S.; Adnan, M.; Noor, M.; Arif, M.; Alam, M.; Khan, I.A.; Ullah, H.; Wahid, F.; Mian, I.A.; Jamal, Y.; et al. Major Constraints for Global Rice Production. In Advances in Rice Research for Abiotic Stress Tolerance; Woodhead Publishing: Sawston, UK, 2019; pp. 1–22. 10. Fuentes, C.; Segundo, A.; Granados, J.C.; Piedrahíta, W. Flora Arvense Asociada Con El Cultivo Del Arroz En El Departamento Del Tolima-Colombia; Bayer Cropscience y Universidad Nacional de Colombia: Bogotá, Colombia, 2006. 11. Puentes, B. Reconocimiento de La Flora Arvense Asociada Al Cultivo Del Arroz (Oryza Sativa L.) En El Departamento Del Tolim. Magister’s Thesis, Universidad Nacional de Colombia, Bogotá, Colombia, 2003. 12. Ramírez, J.; Hoyos, V.; Plaza, G. Phytosociology of Weeds Associated with Rice Crops in the Department of Tolima, Colombia. Agron. Colomb. 2015, 33, 64–73. [CrossRef] 13. Vázquez-García, J.G.; Golmohammadzadeh, S.; Palma-Bautista, C.; Rojano-Delgado, A.M.; Domínguez-Valenzuela, J.A.; Cruz- Hipólito, H.E.; de Prado, R. New Case of False-Star-Grass (Chloris Distichophylla) Population Evolving Glyphosate Resistance. Agronomy 2020, 10, 377. [CrossRef] 14. Giraldo-Cañas, D. Distribución e Invasión de Gramíneas C3 y C4 (Poaceae) En Un Gradiente Altitudinal de Los Andes de Colombia. Caldasia 2010, 32, 65–86. 15. Barroso, A.A.M.; Albrecht, A.J.P.; Albrecht, L.P.; Villetti, H.L.; Orso, G.; de Lima Cavalli, D.A.; Filho, R.V. Competição Entre a Cultura Da Soja e a Planta Daninha Chloris Polydactyla. Rev. do Cent. Univ. Patos Minas 2014, 5, 82–90. 16. Borger, C.P.D.; Riethmuller, G.; Hashem, A. Control of Windmill Grass over the Summer Fallow Increases Wheat Yield. In Proceedings of the 17th Australasian Weeds Conference; Zydenbos, S.M., Ed.; New Zealand Plant Protection Society: Christchurch, New Zealand, 2009; pp. 48–51. Agronomy 2021, 11, 496 13 of 14

17. Llewellyn, R.; Ronning, D.; Ouzman, J.; Walker, S.; Mayfield, A.; Clarke, M. Impact of Weeds on Australian Grain Production: The Cost of Weeds to Australian Grain Growers and the Adoption of Weed Management and Tillage Practices Report for GRDC; GRDC, Grains Research and Development Corporation: Barton, Australia, 2016. 18. Vencill, W.K.; Nichols, R.L.; Webster, T.M.; Soteres, J.K.; Mallory-smith, C.; Burgos, N.R.; Johnson, W.G.; Mcclelland, M.R. Herbicide Resistance: Toward an Understanding of Resistance Development and the Impact of Herbicide-Resistant Crops. Weed Sci. 2012, 60, 2–30. [CrossRef] 19. FEDEARROZ. Manejo Integrado Del Cultivo de Arroz; Produmedios: Bogotá, Colombia, 2014. 20. Ramírez, J.; Hoyos, V.; Plaza, G. Alternativas Herbicidas En El Control de Malezas En El Cultivo de Arroz. In XXI Congreso de la Asociación latinoamericana de Malezas, ALAM y XXXIV Congreso Mexicano de la Ciencia de la Maleza; Asomecima A.C.: Cancún, Mexico, 2013; p. 141. 21. Zimdahl, R.L. Fundamentals of Weed Science, 4th ed.; Elsevier: Amsterdam, The Netherlands, 2013. 22. Duke, S. Overview of Herbicide Mechanisms of Action. Environ. Health Perspect. 1990, 87, 263–271. [CrossRef] 23. Hoyos, V.; Plaza, G.; Caicedo, A.L. Characterization of the phenotypic variability in Colombian weedy rice (Oryza spp.). Weed Sci. 2019, 67, 441–452. [CrossRef] 24. Panozzo, S.; Colauzzi, M.; Scarabel, L.; Collavo, A.; Rosan, V.; Sattin, M. IMAR: An Interactive Web-Based Application for Mapping Herbicide Resistant Weeds. PLoS ONE 2015, 10, 1–12. [CrossRef][PubMed] 25. Zabala, D.; Carranza, N.; Darghan, A.; Plaza, G. Spatial Distribution of Multiple Herbicide Resistance in Echinochloa Colona (L.) Link. Chin. J. Agric. Res. 2019, 79, 576–585. [CrossRef] 26. Frans, R.; Talbert, R.; Marx, D.; Crowley, H. Experimental Design and Techniques for Measuring and Analyzing Plant Responses to Weed Control Practices. In Research Methods in Weed Science; Camper, N.D., Ed.; Southern Weed Science Society: Champaign, IL, USA, 1986; pp. 29–46. 27. Fernández-Moreno, P.T.; Alcantara-De La Cruz, R.; Cruz-Hipólito, H.E.; Rojano-Delgado, A.M.; Travlos, I.; De Prado, R. Non- Target Site Tolerance Mechanisms Describe Tolerance to Glyphosate in Avena Sterilis. Front. Plant Sci. 2016, 7, 1–11. [CrossRef] 28. Bradford, M. A Rapid and Sensitive Method for the Quantitation of Microgram Quantities of Protein Utilizing the Principle of Protein-Dye Binding. Anal. Biochem. 1976, 72, 248–254. [CrossRef] 29. Hatami, Z.M.; Gherekhloo, J.; Rojano-Delgado, A.M.; Osuna, M.D.; Alcántara, R.; Fernández, P.; Sadeghipour, H.R.; de Prado, R. Multiple Mechanisms Increase Levels of Resistance in Rapistrum Rugosum to ALS Herbicides. Front. Plant Sci. 2016, 7, 1–13. [CrossRef] 30. Domínguez-Mendez, R.; Alcántara-de la Cruz, R.; Rojano-Delgado, A.M.; da Silveira, H.M.; Portugal, J.; Cruz-Hipolito, H.E.; De Prado, R. Stacked Traits Conferring Multiple Resistance to Imazamox and Glufosinate in Soft Wheat. Pest Manag. Sci. 2019, 75, 648–657. [CrossRef] 31. Keshtkar, E.; Kudsk, P.; Mesgaran, M.B. Perspective: Common errors in dose–response analysis and how to avoid them. Pest Manag. Sci. 2021. Online ahead of print. [CrossRef] 32. Ritz, C.; Baty, F.; Streibig, J.C.; Gerhard, D. Dose–response Analysis Using R. PLoS ONE 2015, 10, 1–13. [CrossRef] 33. R Core Team. R: A Language and Environment for Statistical Computing; R Foundation for Statistical Computing: Vienna, Austria, 2013; Available online: http://www.rstudio.com/ (accessed on 15 June 2020). 34. Knezevic, S.Z.; Streibig, J.C.; Ritz, C. Utilizing R Software Package for Dose–response Studies: The Concept and Data Analysis. Weed Technol. 2007, 21, 840–848. [CrossRef] 35. Palma-Bautista, C.; Vazquez-Garcia, J.G.; Travlos, I.; Tataridas, A.; Kanatas, P.; Domínguez-Valenzuela, J.A.; De Prado, R. Effect of Adjuvant on Glyphosate Effectiveness, Retention, Absorption and Translocation in Lolium Rigidum and Conyza Canadensis. Plants 2020, 9, 297. [CrossRef] 36. Barroso, A.A.M.; Albrecht, A.J.P.; Dos Reis, F.C.; Placido, H.F.; Toledo, R.E.; Albrecht, L.P.; Filho, R.V. Different Glyphosate Susceptibility in Chloris Polydactyla Accessions. Weed Technol. 2014, 28, 587–591. [CrossRef] 37. Bracamonte, E.R.; Fernández-Moreno, P.T.; Bastida, F.; Osuna, M.D.; Alcántara-de la Cruz, R.; Cruz-Hipolito, H.E.; De Prado, R. Identifying Chloris Species from Cuban Citrus Orchards and Determining Their Glyphosate-Resistance Status. Front. Plant Sci. 2017, 8, 1977. [CrossRef][PubMed] 38. Bracamonte, E.; da Silveira, H.M.; Alcántara-de la Cruz, R.; Domínguez-Valenzuela, J.A.; Cruz-Hipolito, H.E.; De Prado, R. From Tolerance to Resistance: Mechanisms Governing the Differential Response to Glyphosate in Chloris Barbata. Pest Manag. Sci. 2018, 74, 1118–1124. [CrossRef] 39. Brunharo, C.A.; Patterson, E.L.; Carrijo, D.D.R.; de Melo, M.M.S.; Nicolai, M.; Gaines, T.T.A.; Nissen, S.S.J.; Christoffoleti, P.J.P. Confirmation and Mechanism of Glyphosate Resistance in Tall Windmill Grass (Chloris Elata) from Brazil. Pest Manag. Sci. 2016, 72, 1758–1764. [CrossRef][PubMed] 40. Ngo, T.D.; Krishnan, M.; Boutsalis, P.; Gill, G.; Preston, C. Target-Site Mutations Conferring Resistance to Glyphosate in Feathertop Rhodes Grass (Chloris Virgata) Populations in Australia. Pest Manag. Sci. 2017, 74, 1094–1100. [CrossRef] 41. Ngo, T.D.; Malone, J.M.; Boutsalis, P.; Gill, G.; Preston, C. EPSPS Gene Amplification Conferring Resistance to Glyphosate in Windmill Grass (Chloris Truncata) in Australia. Pest Manag. Sci. 2018, 74, 1101–1108. [CrossRef][PubMed] 42. Shaner, D.L.; Nadler-Hassar, T.; Henry, W.B.; Koger, C.H. A Rapid in Vivo Shikimate Accumulation Assay with Excised Leaf Discs. Weed Sci. 2005, 53, 769–774. [CrossRef] Agronomy 2021, 11, 496 14 of 14

43. Wright, A.A.; Rodriguez-Carres, M.; Sasidharan, R.; Koski, L.; Peterson, D.G.; Nandula, V.K.; Ray, J.D.; Bond, J.A.; Shaw, D.R. Multiple Herbicide-Resistant Junglerice (Echinochloa Colona): Identification of Genes Potentially Involved in Resistance through Differential Gene Expression Analysis. Weed Sci. 2018, 66, 347–354. [CrossRef] 44. Tehranchian, P.; Nandula, V.K.; Matzrafi, M.; Jasieniuk, M. Multiple Herbicide Resistance in California Italian Ryegrass (Lolium Perenne Ssp. Multiflorum): Characterization of ALS-Inhibiting Herbicide Resistance. Weed Sci. 2019, 67, 273–280. [CrossRef] 45. Kumar, V.; Jha, P. First Report of Ser653Asn Mutation Endowing High-Level Resistance to Imazamox in Downy Brome (Bromus Tectorum L.). Pest Manag. Sci. 2017, 73, 2585–2591. [CrossRef] 46. Sudianto, E.; Beng-Kah, S.; Ting-Xiang, N.; Saldain, N.E.; Scott, R.C.; Burgos, N.R. Clearfield®Rice: Its Development, Success, and Key Challenges on a Global Perspective. Crop Prot. 2013, 49, 40–51. [CrossRef] 47. Heap, I. The International Survey of Herbicide Resistant Weeds. Available online: http://www.weedscience.org (accessed on 21 June 2020). 48. Rojano-Delgado, A.M.; Portugal, J.M.; Palma-Bautista, C.; Alcántara-de la Cruz, R.; Torra, J.; Alcántara, E.; De Prado, R. Target Site as the Main Mechanism of Resistance to Imazamox in a Euphorbia Heterophylla Biotype. Sci. Rep. 2019, 9, 15423. [CrossRef] 49. Wright, T.R.; Bascomb, N.F.; Sturner, S.F.; Penner, D. Biochemical Mechanism and Molecular Basis for ALS-Inhibiting Herbicide Resistance in Sugarbeet (Beta Vulgaris) Somatic Cell Selections. Weed Sci. 1998, 46, 13–23. [CrossRef] 50. Iwakami, S.; Shimono, Y.; Manabe, Y.; Endo, M.; Shibaike, H.; Uchino, A.; Tominaga, T. Copy Number Variation in Acetolactate Synthase Genes of Thifensulfuron-Methyl Resistant Alopecurus Aequalis (Shortawn Foxtail) Accessions in Japan. Front. Plant Sci. 2017, 8, 254. [CrossRef] 51. Wang, C.J.; Liu, Z.Q. Foliar Uptake of Pesticides-Present Status and Future Challenge. Pesticide Biochem. Phys. 2007, 87, 1–8. [CrossRef] 52. Ortiz, T.; Fuentes, C.L. Determinación de La Resistencia de Poblaciones de Murdannia Nudiflora (L.) Brenan (Piñita) Al Herbicida Metsulfuron-Metil Mediante Una Metodología Bioquímica Indirecta de Diagnóstico Rápido; Universidad Nacional de Colombia: Bogotá, Colombia, 2002. 53. Plaza, G.; Hernandez, F. Effect of Zone and Crops Rotation on Ischaemum Rugosum and Resistance to Bispyribac-Sodium in Ariari, Colombia. Planta Daninha 2014, 32, 591–599. [CrossRef] 54. Peng, Q.; Han, H.; Yang, X.; Bai, L.; Yu, Q.; Powles, S.B. Quinclorac Resistance in Echinochloa Crus-Galli from China. Rice Sci. 2019, 26, 300–308. [CrossRef] 55. Nunes, A.L.; Vidal, R.A.; Trezzi, M.M.; Kalsing, A.; Goulart, I.C.G.R. Herbicidas No Controle de Chloris Distichophylla (Falso- Capim-de-Rhodes). Rev. Bras. Herbic. 2007, 6, 13. [CrossRef] 56. Aguiar, A.C.; de Cutti, L.; Silva, D.; da Kaspary, T.; Muraro, D.; Rieder, E.; Rigon, C. Avaliação de Herbicidas Para o Controle de Chloris Distichophylla. Agrotrópica 2017, 29, 69–74. [CrossRef] 57. Widderick, M.; McLean, A. Optimal Intervals Differ for Double Knock Application of Paraquat after Glyphosate or Haloxyfop for Improved Control of Echinochloa Colona, Chloris Virgata and Chloris Truncata. Crop Prot. 2018, 113, 1–5. [CrossRef] 58. Davidson, B.; Cook, T.; Chauhan, B.S. Alternative Options to Glyphosate for Control of Large Echinochloa Colona and Chloris Virgata Plants in Cropping Fallows. Plants 2019, 8, 245. [CrossRef] 59. Peterson, M.A.; Collavo, A.; Ovejero, R.; Shivrain, V.; Walsh, M.J. The Challenge of Herbicide Resistance around the World: A Current Summary. Pest Manag. Sci. 2018, 74, 2246–2259. [CrossRef]