Grain sorghum is an annual C4 grass crop that is highly efficient in the use of solar energy and water and therefore a key component of cropping systems in the dry regions of the Great Plains (Staggenborg et al. Reference Staggenborg, Dhuyvetter and Gordon2008). In spite of its economic potential and food value, sorghum acres have declined in many parts of the United States (United States Department of Agriculture–National Agricultural Statistics Service 2016), due in part to the existence of few options for weed management. POST herbicides labeled for grain sorghum have limited activity on grasses. Consequently, PRE herbicides are the main option for annual grass control in grain sorghum (Hennigh et al. Reference Hennigh, Al-Khatib and Tuinstra2010). However, grain sorghum is often grown in dry environments under rainfed conditions, and the absence of adequate soil moisture often reduces the activation and efficacy of PRE herbicides (Hennigh et al. Reference Hennigh, Al-Khatib and Tuinstra2010).
In 2004 an acetolactate synthase (ALS)-resistant shattercane population was confirmed in Kansas. Using traditional breeding, the ALS-resistance gene was introgressed into grain sorghum (Tuinstra and Al-Khatib Reference Tuinstra and Al-Khatib2008). DuPont® has obtained the license of the ALS herbicide tolerance trait and has branded the technology as “Inzen”. Inzen sorghum carries a double mutation in the ALS gene, Val560Ile and Trp574Leu (Tuinstra and Al-Khatib Reference Tuinstra and Al-Khatib2008), which confers high levels of tolerance to herbicides in the ALS sulfonylurea (SU) and imidazolinone (IMI) families (Werle et al. Reference Werle, Jhala, Yerka, Dille and Lindquist2016a). The Trp574Leu mutation is one of the most common ALS amino acid substitutions, conferring high levels of resistance to ALS inhibitors in the SU and IMI families (Tranel et al. Reference Tranel, Wright and Heap2016). To our knowledge, the Val560Ile substitution has not been reported to confer resistance to ALS inhibitors in weed species. Nicosulfuron, an active ingredient in the ALS-SU family, is the herbicide to be labeled for POST grass control in Inzen sorghum. The Inzen technology will be commercially available in 2017 (DW Saunders and KL Carlson, personal communication) and has the potential to increase the use of grain sorghum in crop rotations and expand its production in environments where grain sorghum is better adapted than corn (Zea mays L.).
ALS-inhibiting herbicides are effective in small quantities (grams of active ingredient per hectare), have high safety margins on labeled crops, are effective on a broad spectrum of weed species, and have low mammalian toxicity (Tranel and Wright Reference Tranel and Wright2002). Owing to the versatility of these herbicides, the selective pressure applied by their use, and the number of genetic mutations in the ALS gene that can confer resistance, many weed species have evolved resistance to one or multiple ALS inhibitors (Tranel et al. Reference Tranel, Wright and Heap2016). There have been 159 reported ALS inhibitor–resistant weed species worldwide, and 50 are in the United States, including shattercane and johnsongrass (Heap Reference Heap2016). The eight confirmed ALS enzyme sites that confer resistance to ALS-inhibiting herbicides are: Ala122, Pro197, Ala205, Asp376, Arg377, Trp574, Ser653, and Gly654 (Tranel et al. Reference Tranel, Wright and Heap2016). At each site, multiple amino acid substitutions are possible. Substitutions at Pro197 and Trp574 have been the most common across several weed species. The specific amino acid substitution at each site may confer different types and levels of resistance to different ALS herbicide families (Tranel et al. Reference Tranel, Wright and Heap2016). For instance, substitution of Ala122 to Tyr results in resistance to both IMIs and SUs, whereas substitution of Ala122 to Thr results in resistance to IMIs only. All nine confirmed substitutions in Pro197 confer resistance to the SUs but not necessarily to the IMIs and the other ALS herbicide families (Tranel et al. Reference Tranel, Wright and Heap2016).
Werle et al. (Reference Werle, Jhala, Yerka, Dille and Lindquist2016a) collected 190 shattercane and 59 johnsongrass populations from northern Kansas, northwestern Missouri, and Nebraska and evaluated their potential resistance to two ALS-inhibiting herbicides. Five and four shattercane populations were resistant to imazethapyr and nicosulfuron, respectively. Five and three johnsongrass populations were confirmed resistant to imazethapyr and nicosulfuron, respectively. Moreover, two shattercane and two johnsongrass populations appeared to be cross-resistant to nicosulfuron and imazethapyr. Given the variation in resistance to different ALS-inhibiting herbicides among these populations, we hypothesized that resistance is likely the result of different mutations in the ALS gene. Such a result would also suggest that resistance evolved independently in these populations; i.e., a single ALS-resistance allele was not transferred among populations by seed or pollen flow.
The objectives of this research were to determine whether the ALS mutations present in Inzen sorghum were present in any of the ALS inhibitor–resistant shattercane and johnsongrass populations detected in Nebraska and northern Kansas (Werle et al. Reference Werle, Jhala, Yerka, Dille and Lindquist2016a), and whether these populations are likely to have evolved ALS resistance independently from each other. Since the double mutation (Val560Ile and Trp574Leu) in the ALS gene present in Inzen sorghum originated from an ALS inhibitor–resistant shattercane population and the Trp574Leu has been commonly reported to confer ALS resistance in weeds, we expected that one or both of the mutations in Inzen may be present in some of the ALS inhibitor–resistant populations detected in the survey.
Materials and Methods
Greenhouse Study
All putative ALS inhibitor–resistant populations (populations with at least one individual surviving an application of imazethapyr and/or nicosulfuron applied at the labeled rate) detected in the field screening by Werle et al. (Reference Werle, Jhala, Yerka, Dille and Lindquist2016a) were included in this study with the objective of including a wide range of population phenotypic responses to ALS-inhibiting herbicides (12 shattercane and 12 johnsongrass populations; Table 1). Three susceptible shattercane (S-13, S-125, and S-130), three susceptible johnsongrass (J-14, J-25, and J-52), and conventional (Pioneer 87P06) and Inzen (Pioneer YSA3527) sorghums were included in the experiment as our control populations. The susceptible shattercane and johnsongrass populations were selected from the field screening based on their high susceptibility to all herbicides tested and good germination rates (unpublished data). Plants used in the study were grown from seeds collected in the fall of 2013 (Werle et al. Reference Werle, Jhala, Yerka, Dille and Lindquist2016a).
Shattercane (S-) and johnsongrass (J-) populations evaluated in this study listed by state, county, latitude and longitude coordinates, and crop from which they were collected in the fall of 2013 by Werle et al. (Reference Werle, Jhala, Yerka, Dille and Lindquist2016a).
a Populations collected from non-crop areas.
Glumes of shattercane and johnsongrass seeds were mechanically removed using a rub board, seeds were pregerminated on wet germination paper, and two seedlings with exposed radicles were transplanted to a 3.8-cm-wide by 21-cm-high cone-tainer filled with potting mix (Stuewe & Sons, Tangent, Oregon; Berger BM1 All-Purpose Mix, Berger Peat Moss, Saint-Modeste, Quebec, Canada). Placement of seeds on wet germination paper was considered the starting point of the study (0 d after planting [DAP]; the study started on August 11, 2014). At 7 DAP, plants were thinned to one plant per cone-tainer. At 11 and 18 DAP, 30 ml of a nutrient solution containing 15 g of 20-20-20 fertilizer (Peters General Purpose Fertilizer, Scotts, Marysville, OH) diluted in 3.785 L of water was applied to each cone-tainer. A total of 46 plants from each population were grown. Greenhouse conditions during the study were set at 24/19 C day/night cycle with a 16 h photoperiod provided by metal-halide lamps to supplement ambient daylight. Plants were watered daily.
Two 1 cm leaf disks were collected from the newest expanded leaf from each plant using a hole puncher at 15 DAP. Leaf disks were placed in a 1.2 ml tube, flash frozen in liquid nitrogen, and stored at −20 C until further use. Cone-tainers and tubes were labeled with matching codes identifying individual plants. Twenty-three plants from each population were treated with the field-labeled rate of imazethapyr (70 g ai ha−1; WSSA group 2; IMI family)+crop oil concentrate (COC) at 1.25% v/v+2,017 g ha−1 AMS; the remaining 23 plants were treated with nicosulfuron (35 g ai ha−1; WSSA group 2; SU family)+COC at 1% v/v+2,240 g ha−1 AMS. Herbicide treatments were applied at 21 DAP when sorghum, shattercane, and johnsongrass plants were at the 3- to 4-leaf stage (22 to 30 cm tall). Herbicide treatments were delivered using 140 L ha−1 carrier volume and a TP8001E flat-fan nozzle tip (TeeJet Technologies, Spraying Systems, Wheaton, IL) at 241kPa in a spray chamber (Research Track Sprayer, DeVries, Hollandale, MN).
Visual evaluations of plant growth (VE; on a scale of 1 to 10, as suggested by Anderson et al. [Reference Anderson, Roeth and Martin1998], with 1 being dead and 10 being completely healthy) and plant mortality (% of individuals with VE≤3) data were taken at 21 d after treatment (DAT). Plants with VE 1 to 3, 4 to 7, and 8 to 10 were considered susceptible (S; dead plants), moderately resistant (MR; stunted plants, with the main culm injured or dead but new tillers growing back), and resistant (R; light interveinal chlorosis and/or plant stunting to no detectable injury) to the labeled herbicide rate, respectively (Anderson et al. Reference Anderson, Roeth and Martin1998). VE and mortality data were used to choose the populations and individuals to be used for ALS allele characterization.
Genomic DNA Extraction, PCR Amplification, and ALS Allele Determination
Three plants (2 MR [4≤VE≤7] or R [VE≥8] and 1 S [VE≤3]) from populations segregating for resistance to imazethapyr and/or nicosulfuron were randomly selected for DNA extraction and ALS allele determination. Two randomly selected plants from all aforementioned control populations were included. Frozen leaf samples were ground using a TissueLyser II (Qiagen, Hilden, Germany), and genomic DNA was extracted using the CTAB method (Folsom et al. Reference Folsom, Begcy, Hao, Wang and Walia2014). DNA quantity and quality were assessed with a NanoDrop Spectrophotometer (NanoDrop Technologies, Wilmington, DE) to ensure a minimum of 25 ng µl−1 sample−1 for use in PCR.
Three sets of primers were designed to amplify the ALS regions containing the amino acid substitutions confirmed in Inzen sorghum, based on published sorghum ALS sequence as a template (TA3960_4558; SEQ ID NO:1; Tuinstra and Al-Khatib Reference Tuinstra and Al-Khatib2008; Table 2). These primers were designed to cover the ALS gene sequence containing the Asp376, Arg377, Val560, Trp574, Ser653, and Gly654 sites (amino acid number standardized according to the Arabidopsis thaliana (L.) Heynh (GenBankX51514) sequence; Tranel et al. Reference Tranel, Wright and Heap2016). PCR conditions were as follows: a final volume of 25 µl containing 50 ng of genomic DNA, 0.20 µmol L−1 of each primer, 1.5 mmol L−1 MgCl2, 0.2 mmol L−1 of each dNTP, 1X reaction buffer, and 1 U Phusion high-fidelity DNA polymerase (#F-530S, ThermoFisher Scientific, Waltham, MA) using a Mastercycler ep-gradient thermocycler (Eppendorf, Hamburg, Germany). Amplifications were performed for all sets of primers using the following program: denaturation step of 4 min at 94 C, followed by 35 cycles of a denaturation step at 94 C for 45 s, an annealing step at 60 C for 45 s, an extension step at 72 C for 1.5 min, and then a final extension step at 72 C for 5 min. Amplified sequences ranged from 400 to 500 bp (Table 2). PCR products were run on a 2% agarose gel (Benchmark Scientific, Edison, NJ) stained with SYBR Safe DNA Gel Stain (ThermoFisher Scientific, Waltham, MA), and visualized using the BioDoc-IT Imaging system UV Transilluminator (UVP, Upland, CA) to confirm amplification and sizes of the products. Additional PCR assays were used to screen for Ala122, Pro197, and Ala205, but attempts to design primers that would amplify the 5′ region of the ALS gene containing them were unsuccessful. Amplified PCR products were sequenced by Eurofins Genomics (Eurofins MWG Operon, Louisville, KY) in both forward and reverse directions. Nucleotide sequences from each sample were aligned to the sorghum reference genome using the BLASTN algorithm (Altschul et al. Reference Altschul, Gish, Miller, Myers and Lipman1990). ALS nucleotide and amino acid sequences of interest were aligned using multiple sequence comparison by log-expectation software (MUSCLE; Edgar Reference Edgar2004) and compared with the ALS sequence of Inzen sorghum (Tuinstra and Al-Khatib Reference Tuinstra and Al-Khatib2008).
Primers used for partial amplification of the acetolactate synthase (ALS) gene sequence from shattercane and johnsongrass populations.Footnote a
a Primers were developed by M Gelli and I Dweikat (personal communication) for sequencing the ALS gene of grain sorghum and ALS inhibitor–resistant shattercane populations.
b Amino acid positions correspond to the amino acid sequence of ALS from Arabidopsis thaliana (L.) Heynh (GenBankX51514).
Comparative Analysis of ALS Sequence Variation in Sorghum and Other Panicoideae Species
To assess ALS variation in additional sorghum lines, the ALS gene was de novo assembled from Illumina paired-end sequencing data available in the Sequence Read Archive at National Center for Biotechnology Information, including S. bicolor ssp. drummondii (SRA accession number SRR998968), S. bicolor race ‘guinea-margaritiferum’ (SRR998976), S. propinquum (SRR999027), and S. bicolor ssp. verticilliflorum (SRR999023). Raw Illumina reads were assembled with Velvet, v. 1.2.03 (Zerbino and Birney Reference Zerbino and Birney2008), essentially as described previously (Grewe et al. Reference Grewe, Edger, Keren, Sultan, Pires, Ostersetzer-Biran and Mower2014; Zhu et al. Reference Zhu, Guo, Jain and Mower2014), using a range of Kmer values (33, 41, 51, 61) and expected coverage values (100, 50, 20, 10). ALS genes were identified in each Velvet assembly using the blastn search tool (Camacho et al. Reference Camacho, Coulouris, Avagyan, Ma, Papadopoulus, Bealer and Madden2009) with default parameters. For S. bicolor ssp. bicolor ‘BTx623’, the ALS gene was initially taken from chromosome 4 of the reference genome (Paterson et al. Reference Paterson, Bowers, Bruggmann, Dubchak, Grimwood, Gundlach, Haberer, Hellsten, Mitros, Poliakov, Schmutz, Spannagl, Tang, Wang, Wicker, Bharti, Chapman, Feltus, Gowik, Grigoriev, Lyons, Maher, Martis, Narechania, Otillar, Penning, Salamov, Wang, Zhang, Carpita, Freeling, Gingle, Hash, Keller, Klein, Kresovich, McCann, Ming, Peterson, Mehboob-ur-Rahman, Ware, Westhoff, Mayer, Messing and Rokhsar2009) available in GenBank (gene ID SORBI_004G155800 in GenBank accession number CM000763), but the sequence at the 5′ end of the gene did not align well with other species. Therefore, the ALS gene was also taken from a de novo assembly of Illumina read data (SRA accession number SRR1946846) derived from a ‘BTx623-Rooney’ line (Rizal et al. Reference Rizal, Thakur, Dionora, Karki, Wanchana, Acebron, Larazo, Garcia, Mabilangan, Montecillo, Danila, Mogul, Pablico, Leung, Langdale, Sheehy, Kelly and Quick2015), using the assembly procedure described above. The latter sequence aligned well with other species, including ALS genes from additional panicoid grasses acquired from GenBank, including johnsongrass biotype SJ (GenBank accession number KJ538785), corn (X63553), switchgrass (Panicum virgatum L.) (AC243242), foxtail millet [Setaria italic (L.) Beauv.] (XM_004952503), and zoysiagrass (Zoysia japonica Steud.) (AB513331).
Results and Discussion
Greenhouse Screening
In previous dose–response studies, shattercane populations S-46, S-58, S-63, S-117, and S-179 were confirmed resistant to imazethapyr, and S-58, S-63, S-105, and S-178 to nicosulfuron (Werle et al. Reference Werle, Jhala, Yerka, Dille and Lindquist2016a). Johnsongrass populations J-35, J-36, J-37, J-40, and J-44 were confirmed resistant to imazethapyr, and J-15, J-35, and J-36 to nicosulfuron. Populations S-58, S-63, J-35, and J-36 were cross-resistant to nicosulfuron and imazethapyr. The level of resistance to ALS-inhibiting herbicides varied from 2 to >1,000-fold across populations. Corroborating the dose–response results, in the current study, all confirmed resistant populations included individuals that were either MR (4≤VE≤7) or R (VE ≥8) when treated with the labeled herbicide rate to which they had previously demonstrated resistance (Tables 3 and 4). Moreover, shattercane populations S-31, S-105, and S-113 and johnsongrass populations J-10, J-12, and J-18 had a few MR individuals to imazethapyr (≤2 individuals population−1 with VE≤5). Shattercane population S-134 had one MR individual to nicosulfuron (VE=5). Even though it was not confirmed resistant in our previous studies, shattercane population S-113 had five MR individuals to nicosulfuron (VE 4 and 5), and johnsongrass population J-15 had two MR individuals to imazethapyr (VE 6 and 7). Thus, population J-15 had R individuals to nicosulfuron and also had a low frequency of individuals MR to imazethapyr (i.e., it was cross-resistant to the ALS chemistries). Since resistance alleles were not fixed in most populations (mortality ≠ 0%), these results reflect the baseline response of each population to common ALS chemistries ahead of commercialization of Inzen sorghum.
Phenotypic response (visual evaluation [VE] and mortality [%]) of shattercane populations treated with a field-labeled rate of imazethapyr (70 g ai ha−1) and nicosulfuron (35 g ai ha−1).Footnote a
a Twenty-three shattercane plants from each population were exposed to imazethapyr, and 23 additional plants were exposed to nicosulfuron. Plants with VE ranging from 1 to 3, 4 to 7, and 8 to10 were considered susceptible (dead), moderately resistant (stunted plants, with the main culm dead or injured but new tillers growing back), and resistant (light interveinal chlorosis and/or plant stunting to no detectable injury), respectively, when exposed to the labeled herbicide rate (adapted from Anderson et al. [Reference Anderson, Roeth and Martin1998]). Populations S-13, S-125, and S-130 were included as susceptible controls.
b Min., Avg., and Max. represent the minimum, average, and maximum VE observed for each population, respectively.
Phenotypic response (visual evaluation [VE] and mortality [%]) of johnsongrass populations treated with a field labeled rate of imazethapyr (70 g ai ha−1) and nicosulfuron (35 g ai ha−1).Footnote a
a Twenty-three johnsongrass plants from each population were exposed to imazethapyr, and 23 additional plants were exposed to nicosulfuron. Plants with VE ranging from 1 to 3, 4 to 7, and 8 to10 were considered susceptible (dead), moderately resistant (stunted plants, with the main culm dead or injured but new tillers growing back), and resistant (light interveinal chlorosis and/or plant stunting to no detectable injury), respectively, when exposed to the labeled herbicide rate (adapted from Anderson et al. [Reference Anderson, Roeth and Martin1998]). Populations J-14, J-25, and J-52 were included as susceptible controls.
b Min., Avg., and Max. represent the minimum, average, and maximum VE observed for each population, respectively.
Shattercane populations S-58 and S-179 and johnsongrass populations J-36, J-37, J-40, and J-44 had highly R individuals to imazethapyr (VE≤8; Tables 3 and 4). Shattercane populations S-58 and S-63 and johnsongrass populations J-15, J-35, and J-36 had highly R individuals to nicosulfuron. Since the Trp574Leu mutation has been commonly reported to confer high levels of cross-resistance to IMI and SU herbicides, we suspected that R individuals from populations S-58 and J-36 might be carrying this mutation.
ALS Gene Sequencing
The amino acids encoded by ALS codons 376, 377, 560, 574, 653, and 654 in individuals from populations targeted for ALS allele determination are presented in Tables 5 and 6. The 5′ sequence of the ALS gene containing codons 122, 197, and 205 did not amplify in PCR in any species, even using protocols optimized for high GC%. Sequencing results indicated that the Trp574Leu mutation present in Inzen sorghum was present only in johnsongrass population J-36 (Tables 6 and 7), which was highly resistant to imazethapyr and nicosulfuron. This mutation has been reported in resistant populations across multiple species highly resistant to IMI and SU herbicides (Tranel et al. Reference Tranel, Wright and Heap2016), including two ALS inhibitor–resistant johnsongrass populations detected in cornfields in Chile (Hernández et al. Reference Hernández, León, Fischer, Gebauer, Galdames and Figueroa2015). The Trp574Leu mutation was not detected in all R individuals of J-36 (Table 6), indicating that multiple ALS-resistance mechanisms may be present within this population. Multiple mechanisms of ALS resistance within a population have been reported (Guo et al. 2015).
Phenotype and amino acid encoded by acetolactate synthase (ALS) codons 376, 377, 560, 574, 653, and 654 of selected individuals within ALS inhibitor–resistant and susceptible shattercane populations treated with labeled rate of imazethapyr (70 g ai ha−1) and nicosulfuron (35 g ai ha−1).
a Populations S-13, S-125, and S-130 were included as susceptible controls.
b Abbreviations: S, susceptible; MR, moderately resistant; R, resistant.
c Amino acid positions correspond to the amino acid sequence of ALS from Arabidopsis thaliana (L.) Heynh (GenBankX51514). Bold text denotes an amino acid substitution at the specified codon.
d Only one individual in the population survived the imazethapyr application.
e All plants sprayed with nicosulfuron were resistant.
f Only one individual in the population survived the nicosulfuron application.
Phenotype and amino acid encoded by acetolactate synthase (ALS) codons 376, 377, 560, 574, 653, and 654 of selected individuals within ALS inhibitor–resistant and susceptible johnsongrass populations treated with labeled rate of imazethapyr (70 g ai ha−1) and nicosulfuron (35 g ai ha−1).
a Populations J-14, J-25, and J-52 were included as our susceptible controls.
b Abbreviations: S, susceptible; MR, moderately resistant; R, resistant.
c Amino acid positions correspond to the amino acid sequence of ALS from Arabidopsis thaliana (L.) Heynh (GenBankX51514). Bold text denotes an amino acid substitution at the specified codon.
d Only one individual in the population survived the imazethapyr application.
e Not all resistant individuals screened presented the Trp574Leu mutation. Four additional resistant individuals were screened, and three presented the Trp574Leu mutation.
f All individuals in the population survived imazethapyr application.
Acetolactate synthase (ALS) resistance–conferring mutations detected in one shattercane and one johnsongrass population.
a Nucleotide sequence and the encoded amino acid (in parenthesis) at each codon. Amino acid positions correspond to the amino acid sequence of ALS from Arabidopsis thaliana (L.) Heynh (GenBankX51514). Bold text denotes an amino acid substitution at the specified codon.
b Abbreviations: S, susceptible; R, resistant.
The Val560Ile mutation, also present in Inzen sorghum, was detected in ALS-R individuals of shattercane populations S-105 and S-179 and in S individuals of S-63, S-105, S-125, and S-134 (Table 5). This mutation was also detected in ALS-R and S individuals of johnsongrass population J-35 and in S individuals of population J-52 (Table 6). From these results, we conclude that, by itself, the Val560Ile amino acid substitution does not confer resistance to ALS-inhibiting herbicides. None of our populations presented both mutations simultaneously (Val560Ile and Trp574Leu), as does Inzen sorghum (Tables 5 and 6).
The double mutation present in Inzen sorghum was introgressed from an ALS inhibitor–resistant shattercane population detected in Kansas (Tuinstra and Al-Khatib Reference Tuinstra and Al-Khatib2008), and both amino acid substitutions were individually detected in ALS inhibitor–resistant weedy Sorghum species in the present study. We conclude that commercialization of Inzen technology will not transfer any novel/unprecedented ALS mutations to weedy sorghum relatives sympatric with grain sorghum production areas in the Midwest. However, pollen-mediated gene flow from Inzen sorghum to weedy relatives is expected to increase the frequency of ALS-resistance alleles in weedy populations, which will be selected by continued ALS-inhibitor use and result in rapid evolution of highly resistant populations. Effective weed resistance management strategies will be critical to maintain the efficacy of ALS inhibitors where Inzen sorghum is adopted (Werle et al. Reference Werle, Tenhumberg and Lindquist2016b).
The Ser653Thr mutation was present in individuals R to imazethapyr and absent in S individuals from shattercane population S-179 (Tables 5 and 7). Furthermore, this population was resistant to imazethapyr but susceptible to nicosulfuron (Table 3). This corroborates the findings of Patzoldt and Tranel (Reference Patzoldt and Tranel2007), who reported the Ser653Thr mutation to confer resistance to IMI but not to SU herbicides in a common waterhemp [Amaranthus tuberculatus (Moq.) Sauer] population from Illinois. Beckie et al. (Reference Beckie, Warwick and Sauder2012) also reported the Ser653Thr mutation in an IMI-resistant wild oat (Avena fatua L.) population from western Canada. To our knowledge, this is the first time that the Ser653Thr mutation has been reported in shattercane. No mutations were detected at Asp376, Arg377, and Gly654 in our populations; however, amino acid substitutions at these latter codons are reported to confer additional types and levels of ALS resistance in other weed species (Tranel et al. Reference Tranel, Wright and Heap2016). The current study focused on target-site mutations at Asp376, Arg377, Val560, Trp574, Ser653, and Gly654. Mutations at Ala122, Pro197, and Ala205 (which have also been commonly reported; Tranel et al. Reference Tranel, Wright and Heap2016), unreported/novel mutations at different codons in the ALS gene, and non–target site resistance (i.e., a translocation-based mechanism) could be the mechanisms of resistance in the remaining ALS inhibitor–resistant populations detected in Nebraska and Kansas by Werle et al. (Reference Werle, Jhala, Yerka, Dille and Lindquist2016a). Non–target site ALS resistance has been reported in common waterhemp by Guo et al. (Reference Guo, Riggins, Hausman, Hager, Riechers, Davis and Tranel2015). Our future work includes development of high-throughput assays to characterize ALS mutations in shattercane and johnsongrass populations and to more thoroughly characterize putative structural variation at the 5′ end of the gene, where Ala122, Pro197, and Ala205 reside. All methods will be made publicly available for ongoing screening and monitoring of ALS inhibitor–resistant Sorghum species following commercialization of Inzen technology. We further intend to determine whether non–target site resistance is present in these populations.
Distribution of Resistance
Werle et al. (Reference Werle, Jhala, Yerka, Dille and Lindquist2016a) reported that populations from similar geographic regions had differential responses to two ALS-inhibitor chemistries. The current study correlated differential herbicide responses to known amino acid substitutions within the ALS gene sequence amplified from those populations. For instance, two shattercane populations from Thayer County, NE, S-178 and S-179, were 9 km apart and showed different types of resistance (Figure 1). S-178 was moderately resistant to nicosulfuron and did not contain any of the mutations evaluated in this study. S-179 was resistant to imazethapyr and contained two mutations, Val560Ile and Ser653Thr. Three johnsongrass populations from Buffalo County, NE, J-35, J-36, and J-37, were within a radius of 17 km and showed different types of resistance to ALS inhibitors (Figure 2). J-35 was moderately resistant to imazethapyr and resistant to nicosulfuron and contained the Val560Ile mutation. J-36 was highly resistant to both imazethapyr and nicosulfuron and contained the Trp574Leu mutation. J-37 was resistant only to imazethapyr and did not contain any mutations at the ALS codons evaluated in this study. Together, these results support our initial hypothesis and present evidence that resistance in these populations evolved independently and was not due to a single source spread via seeds or pollen-mediated gene flow. However, the availability of high-throughput genotyping methods that could cost-effectively screen more individuals in the more than 200 populations we collected would be useful to confirm this; development of such technologies is a focus of our ongoing work.
Distribution of shattercane populations from Kansas (KS) and Nebraska (NE) included in this study. Abbreviations: S, population susceptible to all herbicides tested; I, resistant to imazethapyr; N, resistant to nicosulfuron; C, cross-resistant to the ALS herbicides tested (nicosulfuron and imazethapyr); V560I and S653T indicate the populations that carried the Val560Ile and Ser653Thr mutations, respectively. The three gray circles represent the regions in Nebraska (Buffalo, Webster, and Thayer counties) where ALS inhibitor–resistant shattercane populations were detected by Lee et al. (Reference Lee, Martin, Roeth, Johnson and Lee1999).
Distribution of johnsongrass populations from Kansas (KS) and Nebraska (NE) included in this study. S, population susceptible to all herbicides tested; I, resistant to imazethapyr; C, cross-resistant to the ALS herbicides tested (imazethapyr and nicosulfuron); V560I and T574L indicate the populations that carried the Val560Ile and Trp574Leu mutations, respectively.
Independent selection for resistance indicates overreliance on the same herbicide mode of action across a broad geographic region favored progeny of individuals containing naturally occurring mutations that originated at each field/site. Because there are multiple sites in the ALS gene where resistance-conferring mutations can occur (Tranel et al. Reference Tranel, Wright and Heap2016), resistance to ALS inhibitors is an ideal case study to research evolutionary mechanisms giving rise to herbicide-resistant weed populations and the spread of resistance alleles across the landscape. For example, if the same phenotypic response and ALS allele was encountered across populations from the same region, improper management at one or a few sites was likely the initial source of resistance alleles that colonized new fields via seed and/or pollen-mediated gene flow. Subsequent repeated applications of ALS inhibitors at these new sites would have favored plants carrying the migrated resistance alleles until they became established in the population. Using distribution and frequency of glyphosate resistance in common waterhemp populations from more than 100 farms across Illinois, Evans et al. (2016) presented strong evidence that the likelihood and frequency of resistant individuals within a population are inversely correlated to the number of herbicide modes of action used per application per season at each farm. Moreover, the likelihood and frequency of resistant individuals were not correlated to the distance from the nearest field infested with resistant weeds. These findings indicate that the use of a diversified approach (i.e., adopting multiple effective modes of action at each application) can significantly reduce selection pressure favoring herbicide resistance, even though neighboring properties may be infested with resistant weeds. Thus, the management program adopted at each farm will be the key driver for resistance evolution and management in situ.
Lee et al. (Reference Lee, Martin, Roeth, Johnson and Lee1999) reported ALS inhibitor–resistant shattercane populations in Buffalo, Webster, and Thayer counties of Nebraska. Resistance was still present in 2013 in two of these counties (Buffalo and Thayer). ALS inhibitor–resistant shattercane and johnsongrass were also detected in other areas of Nebraska and Kansas where ALS-inhibiting herbicides were commonly used prior to the introduction of glyphosate-tolerant crops (Figures 1 and 2). This is an indicator that target-site ALS resistance has little to no ecological fitness cost to weedy populations in the absence of selection by ALS-inhibiting herbicides (i.e., the amino acid substitutions identified herein are neutral mutations), corroborating observations of Davis et al. (Reference Davis, Kruger, Stachler, Loux and Johnson2009), Park et al. (Reference Park, Mallory-Smith, Ball and Muellar-Warrant2004), and Sibony and Rubin (Reference Sibony and Rubin2003). Cost-effective high-throughput genotyping is needed to facilitate more quantitative estimates of fitness costs associated with R alleles in these populations by directly monitoring changes in their frequencies over wide geographies and time.
The results of this research indicate that if growers observed ALS inhibitor–resistant shattercane and/or johnsongrass in their fields in the past, and these species are still present, they are likely to carry resistance alleles. Moreover, we found evidence that resistant populations across common geographical regions evolved resistance independently. Thus, if growers adopt Inzen technology, shattercane and johnsongrass should be properly managed prior to and following its adoption. Use of ALS-inhibiting herbicides in Inzen sorghum will favor weeds that are carrying an ALS-resistance allele. Under continuous use of ALS inhibitors, R individuals (heterozygous or homozygous for resistance alleles) will survive and reproduce, while most S individuals will be killed; hence, the frequency of R individuals in the population will increase until most are resistant, and the technology will rapidly lose value. Moreover, if surviving plants (either resistant individuals or escapes) are present at the end of the season, crop-to-weed gene flow may have occurred. If so, new resistance alleles will be introduced into the weedy sorghum population and the individuals carrying it would be expected to survive and reproduce following application of ALS inhibitors, as described earlier.
Modeling work in shattercane has indicated that crop rotation and proper management with effective herbicides during non-sorghum years (i.e., glyphosate and clethodim) will be key strategies to postpone fixation of the resistance alleles in shattercane and maintain its population density at low levels following deployment of Inzen technology (Werle et al. Reference Werle, Tenhumberg and Lindquist2016b). During non-sorghum years, herbicides from multiple effective modes of action should be considered for shattercane and johnsongrass control and to reduce the likelihood of resistance evolution to alternative herbicide modes of action (Evans et al. 2016; Norsworthy et al. Reference Norsworthy, Ward, Shaw, Llewellyn, Nichols, Webster, Bradley, Frisvold, Powles, Burgos, Witt and Barrett2012). Alternative strategies such as interrow cultivation, rope wick herbicide application (using non-ALS herbicides), and/or rogueing surviving resistant or escape weeds before flowering may also play an important role in managing ALS resistance. These strategies can reduce both the likelihood of pollen-mediated gene flow from Inzen to weedy Sorghum species and seedbank replenishment with resistance alleles (Goulart et al. Reference Goulart, Pacheco, Nunes and Merotto2012; Roeth et al. Reference Roeth, Martin and Klein1994).
Survey of ALS Variation in Wild Sorghum and Other Panicoid Grasses
To assess variation in the ALS gene more broadly, the gene sequence was aligned from an array of sorghum lines and more diverse panicoid grasses, including S. bicolor ‘BTx623’, S. bicolor ssp. drummondii, S. bicolor race ‘guinea-margaritiferum’, S. propinquum, S. bicolor ssp. verticilliflorum, johnsongrass, switchgrass, foxtail millet, corn, and zoysiagrass (Supplementary Figure 1). This alignment revealed a few unexpected results. First, the 5′ portion of the ALS gene from the S. bicolor ‘BTx623’ reference genome, which was used for primer design in PCR-based surveys of ALS codons, was found to be nonhomologous to the 5′ ALS sequences from other panicoid grasses or to the ALS gene that was de novo assembled in this study using the ‘BTx623-Rooney’ resequencing data generated by Rizal et al. (Reference Rizal, Thakur, Dionora, Karki, Wanchana, Acebron, Larazo, Garcia, Mabilangan, Montecillo, Danila, Mogul, Pablico, Leung, Langdale, Sheehy, Kelly and Quick2015). In contrast, the 5′ portion of the ALS gene from the de novo assembled ‘BTx623-Rooney’ sequence matches well with other panicoid grasses. These results suggest that the ALS gene from the reference sequence available in GenBank for S. bicolor ‘BTx623’ may not be correct. The similarity of the ALS sequence from the ‘BTx623-Rooney’ data to other panicoid grasses suggests that this sequence is more accurate.
Second, the 5′ end of the ALS gene from most wild Sorghum species, was not recovered from the de novo assemblies (Figure 3). To rule out issues with assembly, the raw sequence reads generated from each of the wild Sorghum species resequencing projects were mapped to the ‘BTx623-Rooney’ and corn ALS gene sequences. No reads were detected that mapped to 5′ gene regions missing from the wild Sorghum species. This result suggests that the 5′ portion of the gene is truncated in the wild species but not in ‘BTx623’, indicating presence/absence variation among ALS genes in the genus and a lack of Ala122, Pro197, and Ala205 codons in shattercane and johnsongrass. Alternatively, the high GC% in the 5′ portion of the ALS gene may cause biased underrepresentation in the resequencing data. Regardless of the reason, Illumina-based resequencing approaches may not be reliable for detection of SNPs in the 5′ region of the ALS gene. PCR-based approaches, optimized for high GC% templates and using the ‘BTx623-Rooney’ template, will be needed to assess whether the 5′ portion of the ALS gene is truncated in wild Sorghum species and to score SNPs in this region if it is indeed present.
Sequence variation among ALS genes from cultivated, wild, and weedy Sorghum. Shown is a summary of the variation detected among Sorghum species from the ALS alignment in Supplementary Figure 1. Abbreviated names correspond to the full species names listed in “Materials and Methods.” All positions exhibiting sequence variation in at least one Sorghum species are marked on the ALS gene map at top (drawn to scale), and the nucleotides found at that position for all Sorghum species are listed below. Position numbers correspond to the ‘BTx623’ gene sequence that was de novo assembled from the Illumina sequence data (see “Materials and Methods”). All other positions in the alignment were identical among the Sorghum species. The 5′ truncations in the ALS gene of most Sorghum species are shaded in gray, and the extent of each truncation is labeled with nucleotide positions. Positions of known resistance mutations are shown above the gene and marked with a triangle; these position numbers correspond to the Arabidopsis thaliana reference gene (Tranel et al. Reference Tranel, Wright and Heap2016).
Acknowledgments
The authors would like to acknowledge Bret Raush and Roberto Martins for their assistance with greenhouse activities. David Saunders and Kenneth Carlson from DuPont® provided valuable technical support to this research. This project was funded by the United Sorghum Checkoff Program (USCP: CI008-13).
Supplementary material
To view supplementary material for this article, please visit https://doi.org/10.1614/WS-D-16-00095.1
