Introduction

Littleseed canarygrass (Phalaris minor Retz.) is the most dominant winter season weed in wheat and widely distributed in wheat growing regions of the world. This weed has been reported from Macronesia to Mediterranean, Irano-Turanic and Saharo-Sindic regions, eastern and South Africa, North and South America, Australia and the Far East (Singh et al. 1999). In India, it is the major weed of the north-western and eastern Indo-Gangetic Plains (Chhokar and Sharma 2008). Up until the early 1990s, P. minor was effectively controlled by isoproturon, a substituted urea herbicide, but after long period of continuous and heavy spraying along with poor application rates, spray techniques and timing led to the evolution of isoproturon resistance in P. minor (Malik and Singh 1995; Chhokar and Malik 2002). In 1997–1978, four alternative herbicides (sulfosulfuron, clodinafop, fenoxaprop and tralkoxydim) were recommended for its control and the majority of farmers accepted clodinafop due to excellent crop safety and efficacy against this weed. The excessive dependence on clodinafop resulted in evolution of weed resistance against this herbicide. At present, this weed has evolved multiple herbicide resistance across three modes of actions: photosynthesis at the photosystem II site A, acetyl CoA carboxylase and acetolactate synthase inhibition (Chhokar and Sharma 2008). Herbicide resistance in weeds is an evolutionary process and its dynamics and impact are dependent on several factors such as genetics and biology of weeds along with herbicidal, operational and other biological components (Powels and Yu 2010). There are currently 418 unique cases (species x site of action) of herbicide-resistant weeds globally, with 224 species (129 dicots and 95 monocots). Weeds have evolved resistance to 21 of the 25 known herbicide sites of action and to 149 different herbicides. Herbicide-resistant weeds have been reported in 73 crops in 61 countries (Heap 2014).

Aryloxyphenoxypropionate (APP) and cyclohexanedione (CHD) herbicides inhibit plastid form of acetyl-CoA carboxylase by blocking the fatty acid biosynthesis which results in disruption of cell membrane integrity and consequently causing metabolite leakage and rapid plant death (Devine and Shimabukuro 1994). Acetyl-coenzyme A carboxylase (ACCase) (EC.6.4.1.2) is a key enzyme in fatty acid biosynthesis catalyzing ATP-dependent carboxylation of acetyl-CoA to malonyl-CoA. All ACCase isoforms contain three distinct functional domains: the biotin carboxyl carrier (BCC) as structural domain, and the biotin carboxylase (BC) and the carboxyl transferase (CT) domains as catalytic domains (Nikolau et al. 2003). The ACCase enzyme activity is inhibited by APP and CHD herbicides by binding within the CT domain of the plastidic ACCase in susceptible plant species and thus the CT domain of the ACCase gene determines the herbicide sensitivity in plants (Nikolskaya et al. 1999). Several point mutations have been reported in the CT domain of plastid-localized ACCase responsible for the enzyme insensitivity to herbicides in several grass weeds (reviewed by Kukorelli et al. 2013; Beckie and Tardif 2012; Powles and Yu 2010). Therefore, the search for mutations endowing ACCase herbicide resistance was conducted by sequencing the CT domain of the plastidic ACCase gene in P. minor. In this study, we elucidated that the amino acid substitutions in CT domain of plastidic ACCase gene are associated with herbicide resistance in P. minor. Allele-specific PCR-based test further confirmed the differentiation of herbicide-resistant and susceptible populations.

Materials and methods

Plant material

Seeds of 53 P. minor populations were collected during April 2013 from the wheat fields in Haryana and Punjab states of India. One population (G-46), an identified susceptible check for clodinafop, was also included in the study. Pot studies were conducted to determine the response of various populations to clodinafop. The pots were filled with soil from a field having previously no infestation of P. minor and well-rotten farm yard manure in 6:1 ratio (v/v) after passing through 2 mm sieve. The pots were frequently irrigated to deplete the soil seed bank, if any before sowing. The seedlings were established by seeding 50–60 seeds at a depth of 2.5 cm. After 2 weeks of emergence, thinning was done to maintain 15 plants per pot. The herbicide was sprayed at 3 leaf stages of P. minor with Knapsack sprayer fitted with flat fan nozzles. Herbicide treatments were clodinafop (Topik 15 WP; Syngenta India Ltd., Mumbai, India) at 0, 30 and 60 g/ha. Four weeks after spraying, the herbicide response was recorded and leaves of different populations were taken for DNA extraction. The leaf sample for DNA extraction were taken from the control (unsprayed) pots for the susceptible biotypes effectively controlled at ½ X dose (0.30 g/ha), whereas the leaf samples of resistant biotypes were taken from plants survived after spray of X (0.60 g/ha) dose of herbicide.

DNA extraction and plastidic ACCase CT domain sequencing

Genomic DNA was extracted from seedlings using CTAB method (Doyle and Doyle 1990). A polymerase chain reaction (PCR) was performed in a 25-μL volume containing 100 ng of genomic DNA, 2.5 μL of 10× Taq PCR buffer, 1.5 mM of MgCl2, 200 μM of each dNTP, 0.2 μM of each primer and 1.0 unit of Taq DNA polymerase. The thermocycling program consisted of an initial denaturation at 94 °C for 4 min, followed by 30 cycles of 45 s at 94 °C, 30 s at 60 °C, 60 s at 72 °C and a final cycle of 5 min at 72 °C in S 1000 Thermal Cycler (Bio-Rad). The amplified product was separated by electrophoresis on 2 % (w/v) agarose gel and stained with ethidium bromide and analyzed under UV light.

The amplicons were purified using HiPurATM agarose gel DNA purification spin kit (HiMedia Laboratories Pvt. Ltd., Mumbai, India) according to the manufacturer’s instructions and sequenced with primers used for amplification from both the directions to minimize the false SNP due to sequencing artifacts. The sequencing was performed by Eurofins Genomics India Pvt. Ltd, Banglore, India). The sequence alignments were done using ClustalW2 (http://www.ebi.ac.uk/Tools/msa/clustalw2/) with default parameters and allele-specific primers were designed for SNPs (Table 1).

Table 1 Primers used for sequencing and allele-specific PCR analysis of mutations

Results and discussion

The variable crop phytotoxicity to clodinafop treatments were observed in the weed populations. The resistant populations were not affected by recommended dose (X dose) of clodinafop (60 g/ha), whereas susceptible populations were effectively controlled by ½ X dose (30 g/ha) of clodinafop (Table 2). The dose–response assays indicated that 29 populations were resistant, 23 populations were susceptible and one population was moderately resistant to clodinafop.

Table 2 Response of various populations of P. minor to clodinafop

To identify the molecular basis of resistance, the CT domain of ACCase gene from five individuals of two resistant and two susceptible populations was sequenced (GenBank accession No. KF770792, KF770793, KF770794 and KF770795). The sequences were aligned with CT domain of plastidic ACCase genes of Alopecurus myosuroides (GenBank accession No. AJ310767). Two non-synonymous mutations were found in the resistant and susceptible biotypes of P. minor (Fig. 1). The nucleotide sequences of one resistant populations differed from susceptible by a single nucleotide substitution of G/T that resulted in substitution of Trp2027 to Cys in the resistant population, whereas a substitution of T/A resulted in substitution of Ile2041 to Asn (numbered according to the Alopecurus myosuroides plastid ACCase) in another resistant population.

Fig. 1
figure 1

Amino acid sequence comparisons of herbicide target site in the CT domain of ACCase gene. Mutations associated with resistance are shown with residue numbering following the full-length A. myosuroides plastid ACCase (GenBank accession No. AJ310767). The substitution found in the two resistant populations of Phalaris minor (R1 and R2) in comparison with two susceptible populations (S1 and S2) is highlighted at amino acid position at 2027 and 2041

Based on the sequence analysis results for the mutation site, allele-specific PCR was designed from the position of base substitution to further characterize resistant and susceptible populations (Table 1). The rationale in designing the primers was based on the premise that the 3′-terminal positions ought to be unique for the herbicide-resistant biotype. The allele-specific primers were tested on 53 populations which were phenotyped for herbicide resistance. PCR fragment of 143 bp size was obtained from seven resistant populations with primer pair PM2027F/PM2027R associated with Trp2027 to Cys mutation, whereas no PCR product was amplified in susceptible populations (Fig. 2a). Similarly, a 221 bp DNA fragment was amplified from 15 resistant populations associated with Ile2041 to Asn mutations with PM2041F/PM2014R primer pair (Fig. 2b). Two populations (P49 and P54) found to possess both the point mutations based on PCR products. However, the remaining 10 resistant populations were not found to endow these point mutations associated with clodinafop resistance and may possess other mutations responsible for herbicide resistance.

Fig. 2
figure 2

Allele-specific PCR for ACCase mutations, a Trp2027 to Cys and b Ile2041 to Asn in herbicide-resistant populations of P. minor. M 100 bp DNA ladder, R resistant population, S susceptible population

Twelve target site mutations (amino acid substitutions) in the ACCase gene have been documented till date in grass weed species (Beckie and Tardif 2012; Kaundun et al. 2013). The Trp2027 to Cys substitution has also been reported in Iranian P. minor populations to endow resistance to ACCase inhibitors (Gherekhloo et al. 2012) and the Ile2041 to Asn mutation has been reported in awned canary-grass (Phalaris paradoxa) in Israel (Hochberg et al. 2009). The Trp2027Cys and Ile2041Asn mutations confer resistance to APPs (fenoxaprop, clodinafop, haloxyfop). The Trp2027Cys mutation also confers resistance to pinoxaden, whereas Ile2041Asn pinoxaden may confer moderate resistance to pinoxaden. The both mutations were not found associated with resistance to CHDs (Petit et al. 2009; Scarabel et al. 2011). The experiments with yeast gene-replacement strains confirmed that single amino acid changes in Trp2027–Cys and Ile2041–Asn confer strong resistance to APPs and mild resistance to CHDs (Liu et al. 2007). The three-dimensional model of CT-herbicide complex in black-grass revealed that the Ile2041 to Asn substitution interferes with herbicide binding because of change in APP binding site (Délye et al. 2005). The Trp2027 to Cys substitution did not interfere with APP binding but resulted in small allosteric changes which might hamper the access of herbicide to the binding site (Délye et al. 2005). Another computational study on Trp2027 to Cys, Ile2041 to Asn, Asp2078 to Gly, and Gly2096 to Ala mutations suggested a large effect on conformation of the binding pocket and the hydrogen bonding interactions. The mutant-type ACCase has a lower affinity for inhibitor binding than the wild-type enzyme, which account for the molecular basis of herbicide resistance (Zhu et al. 2009).

Resistance to herbicides in weeds is increasing rapidly worldwide and threatening global food security. Resistance has now been reported to all major herbicide modes of action despite the development of resistance management strategies in the 1990s. Herbicide resistance is now widely recognized as the result of the adaptive evolution of weed populations to the intensive selection pressure exerted by herbicides. The least herbicide-sensitive individuals repeatedly sprayed with herbicide have a selective advantage in the weed populations and thus increase in frequency until populations shift towards a predominance of herbicide-resistant individuals (Délye et al. 2013). With patents expiring on many ACC inhibitors worldwide, greater usage of these herbicides as a consequence of falling prices is to be expected in the future and the projected usage trend will be countered by ever-increasing incidence of resistance to herbicides (Beckie and Tardif 2012). Therefore, an efficient and rapid diagnosis of resistance is essential to maintain herbicide efficacy by preventing further resistance selection when resistance has evolved in a weed population and to avoid ineffective herbicide applications.

Conclusion

The continuous adoption of rice–wheat cropping system in wheat growing regions has led to the problem of Phalaris minor as a troublesome weed of wheat causing yield reductions. Reliable, fast, simple detection of herbicide resistance is necessary for farmers to adopt timely alternative herbicide application strategies to prevent further spread of herbicide-resistant weeds. DNA-based diagnostic markers have the advantage of quickly detecting resistant plants compared with conducting pot assays, which are time and space consuming, and labor intensive. The primary aim of the study was to find the mutations in CT domain of plastidic ACCase gene conferring herbicide resistance in P. minor. The allele-specific PCR marker developed based on SNP will help in identification clodinafop-resistant and susceptible populations.