Palmer amaranth was reported in Brazil for the first time in 2015. It was found growing in cotton (Gossypium hirsutum L.) fields in Mato Grosso State (Andrade Júnior et al. Reference Andrade Júnior, Cavaenaghi, Guimarães and Carvalho2015; Carvalho et al. Reference Carvalho, Goncalves Netto, Nicolai, Cavenaghi, Lopez-Ovejero and Christoffoleti2015). Palmer amaranth is rarely found in South American countries; however, recent surveys conducted in Argentina have found that Palmer amaranth is established and problematic in southern Córdoba and San Luis states in soybean [Glycine max (L.) Merr.], peanuts (Arachis hypogaea L.), sorghum [Sorghum bicolor (L.) Moench], and corn (Zea mays L.) (Morichetti et al. Reference Morichetti, Cantero, Núñez, Barboza, Amuchastegui and Ferrell2013). Palmer amaranth is native to the United States and is originally from semi-arid regions (Sauer Reference Sauer1957).
Before Palmer amaranth’s recent introduction, Brazilian weed scientists reported 10 Amaranthus species (Kissman and Groth Reference Kissman and Groth1999), including low amaranth (Amaranthus deflexus L.), smooth pigweed (Amaranthus hybridus L.), spiny amaranth (Amaranthus spinosus L.), redroot pigweed (Amaranthus retroflexus L.), and slender amaranth (Amaranthus viridis L.) (Carvalho et al. Reference Carvalho, López-Ovejero and Christoffoleti2008). Palmer amaranth can be distinguished from other species by the absence of pubescence on the stem, a petiole longer than the leaf blade, and the presence of slightly spiny structures on the female flowers (Sauer Reference Sauer1957). Palmer amaranth is dioecious (Sauer Reference Sauer1957), and no other dioecious Amaranthus species are known to occur in Brazil. This flowering structure ensures cross-pollination (Franssen et al. Reference Franssen, Skinner, Al-Khatib, Horak and Kulakow2001) and high genetic variability, factors that contribute to its adaptive and evolutionary success (Ward et al. Reference Ward, Webster and Steckel2013).
Palmer amaranth is an annual dicotyledonous species with C4 photosynthesis and is able to survive extreme conditions of low humidity and high temperatures. It is a problematic species because it is highly competitive with agricultural crops (Ward et al. Reference Ward, Webster and Steckel2013). Palmer amaranth has become one of the most important weeds in cotton and soybean fields in the United States, especially since many populations have multiple herbicide resistance (Nandula et al. Reference Nandula, Reddy, Koger, Poston, Rimando, Duke, Bond and Ribeiro2012; Sosnoskie et al. Reference Sosnoskie, Kichler, Wallace and Culpepper2011). A major problem in managing Palmer amaranth is the rapid selection and the potential for rapid dispersion of herbicide resistance.
Palmer amaranth introduced in Brazil is resistant to glyphosate, requiring doses higher than 4,500 g ae ha−1 to reduce plant growth by 80%, a threshold at which control with glyphosate is no longer considered economically viable (Carvalho et al. Reference Carvalho, Goncalves Netto, Nicolai, Cavenaghi, Lopez-Ovejero and Christoffoleti2015). Dose–response studies also confirmed that these populations were cross-resistant to the acetolactate synthase (ALS) inhibitors chlorimuron, imazethapyr, and cloransulan, confirming a case of multiple resistance (Gonçalves Netto et al. Reference Gonçalves Netto, Nicolai, Carvalho, Borgato and Christoffoleti2016).
Given the importance of correct species identification and determining herbicide response to inform appropriate management decisions, the objectives of this research were to (1) confirm the identification of the new Amaranthus species discovered in Brazil; (2) confirm and characterize the multiple resistance to glyphosate and ALS inhibitor herbicides; and (3) identify the mechanisms conferring ALS and glyphosate resistance in the Brazilian population.
Materials and Methods
Plant Material
The glyphosate-resistant (BR-R) Palmer amaranth population was collected from a field site in Ipiranga do Norte, Mato Grosso, Brazil. The glyphosate-susceptible (GA-S) Palmer amaranth population was originally collected in 2004 from the University of Georgia Ponder Farm Research Station (Culpepper et al. Reference Culpepper, Grey, Vencill, Kichler, Webster, Brown, York, Davis and Hanna2006). A known tall waterhemp population from Nebraska was used for species identification (Bernards et al. Reference Bernards, Crespo, Kruger, Gaussoin and Tranel2012).
Species-Diagnostic Marker
Tall waterhemp is another dioecious species in the Amaranthus genus but is not known to be present in Brazil. Additionally, a single-nucleotide polymorphism in the ALS gene has been used to genetically identify tall waterhemp and Palmer amaranth (Tranel et al. Reference Tranel, Wassom, Jeschke and Rayburn2002). To determine whether the dioecious Amaranthus individuals collected in Brazil were Palmer amaranth or tall waterhemp, a genotyping protocol was developed using the ALS polymorphism. Approximately 50 mg of young leaf tissue from three untreated GA-S individuals, six untreated BR-R individuals, and three known tall waterhemp individuals were used for DNA extraction using a modified cetyltrimethylammonium bromide (CTAB) extraction protocol (Doyle Reference Doyle1991). Samples were placed in tubes, a metal bead was added, and then the tubes were frozen in liquid nitrogen. The samples were ground using a Qiagen TissueLyser II (Qiagen, Valencia, CA) for 1 min at 30 oscillations s−1. The ground tissue was incubated with 500 µl of 2×CTAB buffer with 4 µl of 2-mercaptoethanol at 50 C for 15 min. The suspension was then incubated for 15 min with 500 µl of 24:1 chloroform:isoamyl alcohol with gentle agitation and then centrifuged for 15 min at 15,000× g. The aqueous phase was removed and reseparated using another 500 µl of 24:1 chloroform:isoamyl alcohol and was centrifuged for 5 min at 15,000× g. The aqueous phase was once again removed and then precipitated with 50 µl sodium acetate (3M, pH 5.2) and 1,650 µl of 100% ethanol. After 15 min at room temperature, samples were centrifuged for 15,000 × g for 15 min. All liquid was removed, and the pellets were rinsed with 70% ethanol and allowed to dry. Dry pellets were resuspended in water. DNA concentration and quality were determined using a micro-spectrophotometer (NanoDrop 2000 Spectrophotometer, Thermo Fisher Scientific, Wilmington, DE).
Amaranthus KASP Genotyping
To determine whether individuals in the BR-R population were Palmer amaranth or tall waterhemp, a Kompetitive Allele Specific PCR (KASP™) assay was developed to genotype a species-diagnostic single-nucleotide polymorphism (SNP) located at base pair 678 in the ALS coding sequence (Tranel et al. Reference Tranel, Wassom, Jeschke and Rayburn2002). The assay was performed using six control individuals, (three GA-S Palmer amaranth individuals, three Nebraska tall waterhemp individuals) and six untreated individuals from the BR-R population. SNP678 is a cytosine (C) in tall waterhemp individuals and a thymine (T) in Palmer amaranth individuals. Two species-diagnostic forward primers for SNP678 were developed that were identical, except the final 3′ nucleotide, which pairs with SNP678. Additionally, each forward primer contained nucleotides at its 5′ end specific for either a HEX- or FAM-labeled oligo contained in the KASP Master Mix (LGC Genomics, Beverly, MA) (tall waterhemp forward primer: 5′-GAAGGTGACCAAGTTCATGCTAAAAAGAAAGCTTCCTTAACAATTCTAGGG-3′; Palmer amaranth forward primer: 5′-GAAGGTCGGAGTCAACGGATTAAAAAGAAAGCTTCCTTAACAATTCTAGGA-3′). For PCR, a universal reverse primer (5′-GTTGAGGTAACTCGATCCATTACTAAGC-3′) was developed that was complementary in both Amaranthus species.
Forward and reverse primers were mixed according to the manufacturer’s recommendations and included 18 µl tall waterhemp forward primer (FAM label) at 12 µM, 18 µl Palmer amaranth forward primer (HEX label) at 12 µM, and 45 µl of universal reverse primer at 30 µM. Primer mix was brought up to 150 µl with 10 mM Tris-HCl (pH 8.3). A master mix was then generated from 11.8 µl of primer mix and 432 µl of LGC Genomics Master Mix. Final reactions were mixed in a 96-well, optically clear plate by combining 4 µl of Amaranthus DNA at 5 ng/µl with 4 µl of LGC Genomics Master Mix plus primers. PCR was performed on a CFX Connect (Bio-Rad Laboratories, Hercules, CA) with the following cycling protocol: 94 C for 15 min; followed by 10 cycles of 94 C for 20 s, 61 decreasing to 55 C for 60 s (0.6 C touchdown per cycle); followed by 26 cycles of 94 C for 20 s, and 55 C for 60 s. An endpoint fluorescence reading was taken by cooling the plate to 30 C for 30 s and reading the plate in both the HEX and FAM fluorescent channels. HEX and FAM fluorescence was corrected by removing the background fluorescence observed in a no-template control. Fluorescence was plotted in a two-dimensional scatter plot so that the test BR-R population individuals could be compared with known tall waterhemp and Palmer amaranth samples. Tall waterhemp samples (primers labeled with FAM) were expected to have high fluorescence intensity for FAM but not HEX, while Palmer amaranth samples (primers labeled with HEX) were expected to have high fluorescence intensity for HEX but not FAM. Clustering of the test BR-R individuals with either high FAM or high HEX fluorescence intensity would indicate their identity as tall waterhemp or Palmer amaranth, respectively. Each KASP-genotyped sample was independently confirmed using the EcoRV PCR-RFLP developed by Tranel et al. (Reference Tranel, Wassom, Jeschke and Rayburn2002) (unpublished data).
Greenhouse Glyphosate Dose Response
A dose–response experiment was carried out in the greenhouse of the Weed Research Laboratory at Colorado State University in Fort Collins, CO, to quantify the level of glyphosate resistance. Seeds from the BR-R and GA-S Palmer amaranth populations were planted on 1% agar medium and placed in a refrigerator at 4 C for 7 d. They were then transferred to a germination bench at room temperature with 12/12 h of day/night to stimulate rapid and simultaneous germination. Germinated seedlings were then transplanted into commercial potting soil (Professional Growing Mix, Sun Gro® Horticulture, Vancouver, Canada) in 5 by 5 cm inserts. They were treated with glyphosate at 8- to 10-cm height and kept in a greenhouse where they were maintained at 24±2 C temperatures and 15/9 h day/night photoperiods supplemented with metal-halide lamps (400 µmol m−2 s−1) and watered twice daily. The experiment was arranged in a randomized complete block design with three replicates. Each replicate contained six individuals for each population and dose, and four individuals for each population and dose when the experiment was repeated. A glyphosate dose response was conducted using 0, 0.05, 0.08, 0.2, 0.4, 0.8, 1.6, and 4.8 kg ae ha−1 with commercially formulated glyphosate (potassium salt, Roundup WeatherMax®, Monsanto, St. Louis, MO). When the experiment was repeated, an additional dose of 8 kg glyphosate ha−1 was included. Applications were made using an overhead track sprayer (DeVries Manufacturing, Hollandale, MN) equipped with a flat-fan nozzle tip (TeeJet® 8002EVS, Spraying System, Wheaton, IL) calibrated to deliver 187 L ha−1 of spray solution at 172 kPa. Survival was recorded after 21 d, defined as any plant showing new growth. Dose–response analysis was conducted using the ‘drc’ package in R (Knezevic et al. Reference Knezevic, Streibig and Ritz2007; R Core Team 2015). Survival data (proportion) were analyzed using the three-parameter log-logistic model in the ‘drc’ package:
$$y\,{\equals}\,{D \over {\left[ {1{\plus}\left( {{x \over {{\rm LD50}}}} \right)^{b} } \right]}}$$
where y=survival; x=glyphosate dose (g ae ha−1); D=upper limit; b=slope; and LD50=dose causing 50% reduction in survival.
Shikimate Assay
Twenty individuals from each of the BR-R and the GA-S populations were grown in the greenhouse and tested for glyphosate resistance using an in vivo leaf-disk assay. Three technical replicates (5-mm leaf disks) from each individual per population were sampled, following the procedure described by Shaner et al. (Reference Shaner, Nadler-Hassar, Henry and Koger2005). The excised leaf disks were placed into 96-well microtiter plates containing 10 mM ammonium phosphate buffer and molecular grade glyphosate at the doses of 100, 500, and 1,000 µM. Shikimate levels were read at 380 nm on a fluorescence plate reader (BioTekTM SynergyTM 2 multi-mode microplate reader, Winooski, VT). A shikimate standard curve was used to quantify shikimate accumulation (ng shikimate µl−1) in the samples. Data were analyzed using a t-test to compare shikimate accumulation between BR-R and GA-S.
EPSPS Gene Copy Number
Genomic DNA was used to determine 5-enolpyruvylshikimate-3-phosphate synthase (EPSPS) copy number using real-time quantitative PCR (qPCR). Twenty individuals from each of the GA-S and BR-R populations were grown in small pots, and young leaf tissue was collected from each individual for genomic DNA. The samples were immediately frozen in liquid nitrogen and stored at −80 C. Genomic DNA was extracted using the DNEasy Plant Mini Kit (Qiagen, Valencia, CA) and quantified using a NanoDrop spectrophotometer (Thermo Scientific, Wilmington, DE). DNA concentrations were adjusted to 5 ng µl−1, and primer sets and qPCR conditions were used as previously described (primers ALSF2 and ALSR2, EPSF1 and EPSR8) (Gaines et al. Reference Gaines, Zhang, Wang, Bukun, Chisholm, Shaner, Nissen, Patzoldt, Tranel, Culpepper, Grey, Webster, Vencill, Sammons, Jiang, Preston, Leach and Westra2010). Threshold cycles (Ct) for EPSPS and ALS were recorded by a CFX ConnectTM Real-Time PCR Detection System thermal cycler (Bio-Rad Laboratories, Hercules, CA). Relative EPSPS gene copy number was calculated as 2–ΔCt, with ΔCt=[(Ct, ALS) − (Ct, EPSPS)] (Gaines et al. Reference Gaines, Zhang, Wang, Bukun, Chisholm, Shaner, Nissen, Patzoldt, Tranel, Culpepper, Grey, Webster, Vencill, Sammons, Jiang, Preston, Leach and Westra2010). Triplicate technical replications were used to calculate the mean and standard error of the increase in EPSPS gene copy number relative to ALS.
Single-Dose ALS Testing
Single-dose experiments were conducted to assess resistance to the ALS inhibitors chlorsulfuron, sulfometuron-methyl (both sulfonylureas), and imazethapyr (imidazolinone). These experiments were conducted in the greenhouse at Colorado State University in Fort Collins, CO, under the same conditions as described in the glyphosate dose-response experiment. Individuals from BR-R and GA-S were treated at 8- to 10-cm height. The experiments with sulfonylureas used 28 individuals per population and treatment combination, and the experiments with imazethapyr used 36 individuals for each population. Chlorsulfuron (Glean, DuPont, Wilmington, DE) and sulfometuron-methyl (Oust, Bayer CropScience, Research Triangle Park, NC) were applied at 88 g ai ha−1 and 315 g ai ha−1, respectively. Imazethapyr (Pursuit, BASF, Research Triangle Park, NC) was applied at 61 g ai ha−1 with 1.25% v/v crop oil concentrate. Height (cm), dry weight (g), and survival data were collected 21 d after treatment. The data were analyzed using ANOVA, and LSD with P=0.05 was used for multiple comparison adjustment.
ALS Gene Sequence
Approximately 50 mg of young leaf tissue was sampled from each of three untreated GA-S individuals, six untreated BR-R individuals, nine BR-R individuals that survived 315 g ai ha−1 sulfometuron-methyl, and nine BR-R individuals that survived 88 g ai ha−1 chlorsulfuron. DNA was extracted as described for the species-diagnostic marker. The full-length ALS gene was amplified by PCR using the forward primer: 5′-ATGGCGTCCACTTCAACAAACC-3′ and reverse primer 5′-CTAATAAGCCCTTCTTCCATCACCC -3′. Thirty microliter reactions were mixed following the standard protocol provided with Thermo Scientific Phusion polymerase and 20 ng of template genomic DNA. Reactions were cycled 32 times with the following three-step protocol: 98 C for 10 s, 62 C for 20 s, and 72 C for 90 s. PCR products were run on a 1% agarose gel to verify single band amplification. The expected bands at 2,010 bp were excised from the gel and purified following the standard protocol provided by the QIAquick Gel Extraction Kit from Qiagen. Purified PCR products were sequenced using both the amplification primers listed above and the following four sequencing primers: Seq_FP1 5′-AGTTTGTATTGCCACTTCTGGTCC-3′, Seq_FP2 5′-GAAATCCTCGCCAATGGCTGAC-3′, Seq_RP1 5′- GTCAGCCATTGGCGAGGATTTC-3′, Seq_RP2 5′-TGGACCAGAAGTGGCAATACAAAC-3′. Sanger sequencing reads were analyzed using A Plasmid Editor (aPe, version 2.0.49) and heterozygous base pairs were identified in the sequence trace files by manual inspection. Translated amino acid sequences obtained from BR-R and GA-S were compared with a known susceptible Palmer amaranth ALS amino acid sequence (Molin et al. Reference Molin, Nandula, Wright and Bond2016), GenBank protein accession AMS38337.1.
Results and Discussion
Species-Diagnostic Marker
The genotyping assay used to amplify an SNP within the ALS gene that distinguishes Palmer amaranth from tall waterhemp clearly grouped the BR-R individuals with Palmer amaranth GA-S individuals (Figure 1) due to the high HEX fluorescence intensity produced from the Palmer amaranth HEX-labeled forward primer. Known tall waterhemp individuals were clearly distinguished by the tall waterhemp allele at this SNP position, as shown by high FAM fluorescence intensity produced from the FAM-labeled forward primer specific for tall waterhemp. Therefore, the dioecious Amaranthus population collected from Mato Grosso State, Brazil is Palmer amaranth and not tall waterhemp. The EcoRV PCR-RFLP developed by Tranel et al. (Reference Tranel, Wassom, Jeschke and Rayburn2002) also produced the same species identification as our KASP assay (unpublished data).
Genotyping assay using KASP in which Palmer amaranth forward primers in the KASP assay were labeled with HEX, and tall waterhemp forward primers were labeled with FAM. Clustering of the Brazilian population (BR-R) together with known Palmer amaranth (GA-S) for high HEX fluorescence intensity confirms that BR-R is Palmer amaranth. Known tall waterhemp samples showed expected high FAM fluorescence intensity, and no-template control (NTC) had no fluorescence for HEX or FAM.
Greenhouse Dose–Response Curves
The data from two repeated greenhouse dose–response experiments were combined for analysis. The BR-R population was glyphosate resistant (Table 1; Figure 2), with an LD50 of 3,982 g ha−1. The LD50 for GA-S was 169 g ha−1, resulting in a resistance factor (R/S) of 24 (Table 1; Figure 2). This resistance factor confirms the resistance of the Brazilian Palmer amaranth population to glyphosate and demonstrates that the BR-R population has an LD50 higher than two times the typical commercial glyphosate rate (ranging from 800 to 1,000 g ae ha−1).
Greenhouse glyphosate dose–response curves for plant survival of a glyphosate-resistant Palmer amaranth population from Brazil (BR-R) and glyphosate-susceptible Palmer amaranth from Georgia (GA-S) expressed as the proportion of survivors (Equation 1).
Confirmation of glyphosate resistance in Palmer amaranth from Brazil (BR-R) compared with a known glyphosate-susceptible population from Georgia (GA-S) in two repeated greenhouse dose–response experiments.Footnote a
a Plant survival expressed as a proportion was used in a three-parameter log-logistic equation (Equation 1).
b Upper limit.
c Herbicide dose in g ae ha−1 that causes 50% reduction in survival; standard error in parentheses.
d Slope.
e Ratio of LD50 for BR-R to LD50 for GA-S expressed as R/S resistance factor; standard error in parentheses.
Shikimate Assay
Shikimate is an important intermediate in the biosynthesis of the aromatic amino acids phenylalanine, tyrosine, and tryptophan. EPSPS inhibition by glyphosate results in shikimate accumulation (Herrmann and Weaver Reference Herrmann and Weaver1999; Shaner et al. Reference Shaner, Nadler-Hassar, Henry and Koger2005; Steinrücken and Amrhein Reference Steinrücken and Amrhein1980). There was a clear difference in shikimate accumulation between the two populations tested at all three glyphosate doses (Figure 3), with GA-S accumulating significantly more shikimate than BR-R. Increasing glyphosate doses, for doses of up to 1,000 µM, did not cause shikimate accumulation in BR-R, a clear metabolic marker for glyphosate resistance. The lack of shikimate accumulation in the BR-R plants corroborates results obtained from the dose–response curves (Table 1; Figure 2), with both confirming glyphosate resistance in the BR-R population. These results also confirm the findings of Carvalho et al. (Reference Carvalho, Goncalves Netto, Nicolai, Cavenaghi, Lopez-Ovejero and Christoffoleti2015) reporting glyphosate resistance of this Palmer amaranth population from the state of Mato Grosso, Brazil.
Shikimate accumulation in glyphosate-resistant Palmer amaranth from Brazil (BR-R) and glyphosate-susceptible Palmer amaranth from Georgia (GA-S) at three glyphosate doses. Mean from 20 biological replications with standard deviation; **** P-value<0.0001 between GA-S and BR-R at each dose.
EPSPS Gene Copy Number
The qPCR technique was used to quantify EPSPS gene copy number relative to ALS. Between 1.1 and 1.5 relative EPSPS gene copies were measured in the GA-S population, and between 50 and 179 relative EPSPS gene copies were measured in the BR-R population. Increased EPSPS gene copy number was highly correlated with reduced shikimate accumulation in BR-R individuals, while wild-type, single-copy EPSPS was highly correlated with high shikimate accumulation in GA-S individuals (Figure 4). Individuals in the BR-R population have EPSPS gene duplication that results in EPSPS overexpression as a mechanism of glyphosate resistance, first reported in Palmer amaranth (Gaines et al. Reference Gaines, Zhang, Wang, Bukun, Chisholm, Shaner, Nissen, Patzoldt, Tranel, Culpepper, Grey, Webster, Vencill, Sammons, Jiang, Preston, Leach and Westra2010).
EPSPS relative genomic copy number and shikimate accumulation after treatment of leaf disks with 1,000 µM glyphosate in glyphosate-resistant Palmer amaranth from Brazil (BR-R) and glyphosate-susceptible Palmer amaranth from Georgia (GA-S).
A previously reported glyphosate-resistant Palmer amaranth population from Georgia had a reported LD50 of 1,600 g ha−1 and between 40 and 100 relative EPSPS gene copies (Gaines et al. Reference Gaines, Shaner, Ward, Leach, Preston and Westra2011). The BR-R population had an LD50 of 3,982 g ha−1 (Table 1) and EPSPS gene duplication between 50 and 179 copies, suggesting that glyphosate resistance in BR-R is due to increased EPSPS gene copies. Increased EPSPS gene copy number as a glyphosate resistance mechanism has also been reported in Italian ryegrass [Lolium perenne L. ssp. multiflorum (Lam.) Husnot] (Salas et al. Reference Salas, Dayan, Pan, Watson, Dickson, Scott and Burgos2012), tall waterhemp (Chatham et al. Reference Chatham, Bradley, Kruger, Martin, Owen, Peterson, Mithila and Tranel2015a, Reference Chatham, Wu, Riggins, Hager, Young, Roskamp and Tranel2015b; Lorentz et al. Reference Lorentz, Gaines, Nissen, Westra, Strek, Dehne, Ruiz-Santaella and Beffa2014), spiny amaranth (Nandula et al. Reference Nandula, Wright, Bond, Ray, Eubank and Molin2014), ripgut brome (Bromus diandrus Roth) (Malone et al. Reference Malone, Morran, Shirley, Boutsalis and Preston2016), kochia [Kochia scoparia (L.) Schrad.] (Wiersma et al. Reference Wiersma, Gaines, Preston, Hamilton, Giacomini, Buell, Leach and Westra2015), and goosegrass (Eleusine indica (L.) Gaertn.] (Chen et al. Reference Chen, Huang, Zhang, Wei, Huang, Chen and Wang2015).
Single-Dose ALS Testing
A high percentage of BR-R individuals survived treatment with chlorsulfuron, sulfometuron, and imazethapyr (Table 2). The GA-S population was completely controlled by all three ALS herbicides. Plant height and dry weight also indicated that BR-R individuals were resistant to all three ALS herbicides, while GA-S individuals were susceptible (Table 2). The high survival rate of BR-R after ALS herbicide treatment is consistent with previous observations of high-level ALS herbicide resistance in Palmer amaranth (Burgos et al. Reference Burgos, Kuk and Talbert2001; Guo et al. Reference Guo, Riggins, Hausman, Hager, Riechers, Davis and Tranel2015; Whaley et al. Reference Whaley, Wilson and Westwood2007; Wise et al. Reference Wise, Grey, Prostko, Vencill and Webster2009).
A glyphosate-resistant Palmer amaranth population from Brazil (BR-R) is resistant to sulfonylurea and imidazolinone ALS herbicides.Footnote a
a Plants were treated at 8- to 10-cm height. Survival, height, and dry weight data collected 21 d after treatment for single-dose treatments of chlorsulfuron (88 g ha−1), sulfometuron (315 g ha−1), and imazethapyr (61 g ha−1) on BR-R and GA-S (glyphosate- and ALS-susceptible Palmer amaranth from Georgia). Standard deviation shown in parentheses; n, number of individuals tested per dose; letters within a column indicate significant difference at P=0.05.
ALS Gene Sequencing
Sequencing the ALS gene from both populations resulted in the identification of two independent mutations in the BR-R ALS gene sequence, resulting in a change from tryptophan to leucine at position 574 (W574L) and serine to asparagine at position 653 (S653N) (Table 3; Figure 5). The W574L mutation is known to confer resistance to both imidazolinones and sulfonylureas, while the S653N mutation is known to confer resistance only to imidazolinones (Burgos et al. Reference Burgos, Kuk and Talbert2001; Franssen et al. Reference Franssen, Skinner, Al-Khatib, Horak and Kulakow2001; McCourt et al. Reference McCourt, Pang, King-Scott, Guddat and Duggleby2006; Patzoldt and Tranel Reference Patzoldt and Tranel2007; Powles and Yu Reference Powles and Yu2010; Sprague et al. Reference Sprague, Stoller, Wax and Horak1997; Tranel and Wright Reference Tranel and Wright2002). Nearly all BR-R individuals were either heterozygous or homozygous for W574L, while 10 of 24 sequenced individuals were heterozygous for S653N; none were homozygous for S653N. No individuals carried both W574L and S653N mutations within the same allele. ALS resistance is inherited as a dominant trait (Powles and Yu Reference Powles and Yu2010; Tranel and Wright Reference Tranel and Wright2002), which explains the high survival rate of heterozygous ALS mutants in BR-R. No other ALS mutations were detected, but four BR-R individuals that survived either chlorsulfuron or sulfometuron were homozygous for the susceptible allele at W574, and all four were heterozygous for S653N (Table 3). Since the S653N is not known to confer resistance to sulfonylurea herbicides, these four individuals may have a different, non–target site resistance mechanism. A different and undetected ALS target-site mutation is considered unlikely, as the entire ALS gene was sequenced. All sequenced GA-S individuals were homozygous susceptible for both W574 and S653 (Table 3; Figure 5).
Alignment of ALS amino acid sequences from known ALS-susceptible Palmer amaranth (GenBank AMS38337.1), glyphosate- and ALS-susceptible Palmer amaranth from Georgia (GA-S), and glyphosate- and ALS-resistant Palmer amaranth from Brazil (BR-R) individuals, showing W574L and S653N mutations in BR-R individuals.
Two target-site ALS mutations are present in ALS-resistant Palmer amaranth from Brazil (BR-R).Footnote a
a All BR-R individuals that survived a single-dose treatment with chlorsulfuron or sulfometuron had at least one ALS resistance–conferring allele at position W574 (resistant allele L) or S653 (resistant allele N) of ALS. All individuals from GA-S were homozygous for the susceptible allele at W574 and S653.
b HOMO R, homozygous resistant allele (dark cells); HET, heterozygous (gray cells); HOMO, homozygous susceptible allele (light cells).
In wild radish (Raphanus raphanistrum L.), the S653N mutation confers resistance to the imidazolinones, while homozygous W574L confers resistance to sulfonylureas, imidazolinones, and triazolpirimidines, three chemical families of ALS inhibitors (Yu et al. Reference Yu, Han, Li, Purba, Walsh and Powles2012). The presence of W574L gives high levels of resistance to these three chemical groups in tall waterhemp, while S653N is usually linked to imidazolinone resistance (Patzoldt and Tranel Reference Patzoldt and Tranel2007), as observed here.
Molin et al. (Reference Molin, Nandula, Wright and Bond2016) reported both the W574L and the S653N mutation in Palmer amaranth, and showed the transfer of the W574L mutation from Palmer amaranth to hybrids between Palmer amaranth and spiny amaranth. Resistance to ALS inhibitors was reported in mucronate amaranth (Amaranthus quitensis H.B.K.) and Palmer amaranth from Argentina, with the S653N mutation observed only in mucronate amaranth but not in Palmer amaranth (Berger et al. Reference Berger, Madeira, Ferrell, Gettys, Morichetti, Cantero and Nuñez2016). The study concluded that the Palmer amaranth population in Argentina likely has a different ALS resistance mechanism than target-site mutation. While not definitive, the absence of S653N in Palmer amaranth from Argentina and the presence of both W574L and S653N in Palmer amaranth from Brazil suggest that independent introductions of Palmer amaranth may have occurred in the two countries.
This is the first study confirming through molecular methods the introduction of Palmer amaranth in Brazil and the molecular mechanisms of multiple resistance within this population to glyphosate and ALS inhibitors. The resistance mechanisms are, respectively, increased EPSPS gene copy number and target-site mutations in ALS (W574L and S653N). Both mechanisms confer high resistance levels to these herbicides. Other known glyphosate resistance mechanisms such as vacuole sequestration (Ge et al. Reference Ge, d’Avignon, Ackerman and Sammons2010, Reference Ge, d’Avignon, Ackerman, Collavo, Sattin, Ostrander, Hall, Sammons and Preston2012) and reduced translocation (e.g., Vila-Aiub et al. Reference Vila-Aiub, Balbi, Distefano, Fernandez, Hopp, Yu and Powles2012; Wakelin et al. Reference Wakelin, Lorraine-Colwill and Preston2004) were not investigated. Increased ALS gene expression was also not investigated as a potential resistance mechanism. While these mechanisms have not yet been reported in Palmer amaranth, they cannot be ruled out based on the results of this study. Integrated management practices should be adopted in places where Palmer amaranth is found in Brazil, such as tank-mixing herbicides with different mechanisms of action, using PRE herbicides, crop rotation, and integrating cover crops (e.g., DeVore et al. Reference DeVore, Norsworthy and Brye2013; Price et al. Reference Price, Balkcom, Duzy and Kelton2012) for more effective Palmer amaranth control. Future research should focus on population genetics to determine the geographic route by which Palmer amaranth was introduced in Brazil and how to prevent possible new introductions of this and other species.
