Abstract
Secondary metabolites play an important role in host plant resistance to insects, and insects, in turn, may develop mechanisms to counter plant resistance mechanisms. In this study, we investigated the toxicity of gramine to the cereal aphid Sitobion avenae and some enzymatic responses of S. avenae to this alkaloid. When S. avenae fed on an artificial diet containing gramine, mortality occurred in a dose-dependent manner. The LC50 of gramine was determined to be 1.248 mM. In response to gramine, S. avenae developed increased activities of carboxylesterase and glutathione S-transferase, two important detoxification enzymes. The activities of both enzymes were positively correlated with the concentration of dietary gramine. In addition, the activities of peroxidase and polypheolic oxidase, two important oxidoreductase enzymes in S. avenae, increased in response to gramine; however, catalase activity decreased when insects were exposed to higher levels of dietary gramine. The potential role of gramine in host plant resistance and S. avenae counter-resistance is discussed.
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Introduction
Host plant resistance against insects is recognized as an important component of integrated insect pest management (Gao 1994; Schotzko and Bosque-pérez 2000; Li et al. 2001). Plant resistance is attributed largely to secondary metabolites such as phenolics, nonprotein amino acids, and alkaloids, which are documented to be deleterious to insect herbivores (Manuwoto and Scriber 1985; Ciepiela and Sempruch 1999; Wang et al. 2006).
Many alkaloids are strong deterrents to aphids and other herbivores and have been used as botanical insecticides and/or antixenotic chemicals (Luo et al. 1997; Jiang et al. 1999). Gramine, a simple indole alkaloid found in barley and other crop plants, occurs widely in plants of Gramineae and has a wide range of biological activities against insects, mammals, and bacteria (Corcuera 1984, 1993; Züñiga and Corcuera 1986; Leszczynski et al. 1989).
In the plant–insect ecosystem, insect detoxification enzymes (i.e., esterase and glutathione S-transferase) and oxidoreductases (i.e., polyphenol oxidase, peroxidase, and catalase) are important antiresistant agents against the secondary metabolites found in their host plants. Their role in overcoming plant resistance has been studied extensively in a number of insect species (Gao et al. 1997; Figueroa et al. 1999; Luo and Zhang 2003). However, little is known about the changes of detoxification enzymes and oxidoreductases in aphids in response to gramine.
The present study was conducted to elucidate some of the biochemical mechanism(s) of gramine in host plant resistance and to determine how the English grain aphid, Sitobion avenae (F.), counters this resistance. The specific objectives were (1) to assess the direct toxicity of gramine to S. avenae and (2) to determine activities of detoxification enzymes and oxidoreductases in S. avenae in response to gramine in its diet.
Methods and Materials
Insects
Sitobion avenae nymphs and adults were collected from field-grown wheat and maintained on the aphid-susceptible cultivar “Beijing 411,” under field conditions. Insects over two generations were used for experiments.
Diet Preparation and Gramine Toxicity
To determine gramine toxicity to S. avenae, technical-grade gramine was incorporated into an artificial diet containing the following ingredients: 300 mg agrinine, 50 mg cysteine, 200 mg histidine, 200 mg lysine, 100 mg methionine, 100 mg phenylalanine, 100 mg serine, 100 mg tryptophan, 20 mg tyrosine, 10 mg ascorbic acid, 0.1 mg biotin, 50 mg choline chloride, 1.0 mg folic acid, 10 mg p-aminobenzoic acid, 10 mg nicotinic acid, 2.5 mg pyridoxine HCl, 2.5 mg thianine HCl, 500 mg K3PO4, 200 mg MgCl2.6H2O, 100 ml distilled water, and 25 g sucrose. The pH was adjusted to 6.0 with K3PO4 (Auclair 1965; Kieckhefer and Derr 1967; Chen et al. 2000). Gramine (Kingsley and Keith) was dissolved into the liquid artificial diet to get a range of concentrations (4.0, 2.0, 1.0, 0.5, 0.25, 0.125, and 0.0 mM) for LC50 determination.
To assess effect of gramine on S. avenae detoxification enzymes and oxidoreductases and to ensure sufficient live aphids for biochemical analyses, technical grade gramine was dissolved in the artificial diet to compose four different concentrations (0.025, 0.05, 0.1, and 0.2 mM) below the LC50. A diet containing no gramine was used as the control.
The second–third instar nymphs of S. avenae were fed on the liquid diet held between two layers of Parafilm M® (Auclair 1965). Two layers of stretched Parafilm were placed in a transparent cylindrical Plexiglas tube (height 60 mm and diameter 22 mm) and covered on top with gauze to allow air and humidity exchange. After 72 h of feeding, mortality was determined, and the survivors were collected for analyses of the detoxification enzymes and oxidoreductases.
Detoxification Enzyme Assays
Carboxylesterase (CarE) activity was measured according to the method of Ni and Quisenberry (2003), with modification. Sitobion avenae (50 mg) were homogenized in 0.02 M potassium phosphate buffer (2 ml; pH 7.0) at 0°C. The homogenate was centrifuged (5,000×g at 4°C for 15 min). An aliquot (0.1 ml) of the resulting supernatant was mixed with 0.9 ml of the solution containing a-NA and Fast blue RR salt (10 mg a-NA and 20 mg Fast blue RR salt dissolved in 2 ml acetone, and diluted to 25 ml by adding the above phosphate buffer). The reaction progress was monitored spectrophotometrically at 405 nm.
Glutathione S-transferase (GST) was measured according to Ni and Quisenberry (2003). Frozen S. avenae (50 mg) were homogenized in 0.1 M Tris–HCl buffer (2 ml; pH 8.0) at 0°C. The homogenate was centrifuged (10,000×g at 4°C for 15 min). The assay mixture contained the resulting supernatant (0.1 ml), the above described Tris–HCl buffer (1.4 ml), and reduced glutathione (40 mM; 50 μl). After a preincubation (5 min at 25°C), CDNB (30 mM; 60 μl) was added. Change in absorbance was monitored at 340 nm.
Oxidoreductase Assays
Aphids (50 mg) from each sample were ground in liquid nitrogen and then homogenized in 1 M ice-cold potassium phosphate buffer (1 ml) containing 1% polyvinylpyrrolidone and 1% Triton X-100 at pH 7.0. The homogenate was centrifuged (10,000×g at 4°C for 15 min), and the supernatant was used for analyses of the following three oxidoreductases.
Peroxidase (POD) activity was measured using the method of Hildebrand et al. (1986) and Hori et al. (1997). Enzyme extract (20 μl) was mixed with the substrate containing hydrogen peroxide (30%; 10 μl), guaiacol (18 mM; 300 μl), and hydroxyethylpiperazine ethanesulfonic acid (HEPES) buffer in deionized water (200 mM; pH 7.0; 100 μl). POD activity was estimated from the increase in A 470. The measurement was repeated three times.
Polyphenol oxidase (PPO) activity was determined following the method of Hori et al. (1997). Enzyme extract (20 μl) was mixed with a solution containing 1.6% catechol in HEPES buffer (500 μl), 200 mM HEPES (pH 6.0; 100 μl), and deionized water (380 μl). PPO activity was estimated from the increase in A 470. The analysis was repeated three times.
Catalase (CAT) activity was determined as described by Hildebrand et al. (1986) with minor modification. Enzyme extract (20 μl) was mixed with a solution containing hydrogen peroxide (75 mM; 100 μl), HEPES (200 mM; pH 8.0; 100 μl), and deionized water (780 μl). CAT activity was estimated from the increase in A 240. The analysis was repeated three times.
Total protein content was determined by the Bradford method (Bradford 1976). Absorbance of the reaction mixture was read at 595 nm with a spectrophotometer, and protein content was determined from a standard curve established using known quantities of bovine serum albumin (from Sigma Chemical) and the protein assay reagent.
Statistical Analysis
Toxicity of gramine to S. avenae was subjected to probit analysis using the PriProbit Program V1.6.3 (Sakuma 1998). Analysis of variance was used to analyze the activity data from GST, CarE, POD, PPO, and CAT assays in S. avenae. Means were separated by the least significant difference test (α = 0.05) (SPSS 11.0). Correlation between enzymatic activities and gramine concentrations was determined by correlation test (α = 0.05) (SPSS 11.0).
Results
Gramine Toxicity
Gramine killed S. avenae when the insect was fed with the artificial diet containing higher concentrations of the alkaloid (Fig. 1). After 72 h of feeding, S. avenae mortality followed in a dosage-dependent manner. The LC50 was determined to be 1.248 mM (range 0.947–1.743 mM).
Effect of Gramine Enzyme Activity
Total protein content of S. avenae varied after the aphids fed on the artificial diet containing gramine at various concentrations (Fig. 2). With the exception of aphids that fed on 0.025 mM gramine, higher levels of total protein were found in all treatments compared to the control (df = 4, 10, F = 275.34, P < 0.001).
GST activity in S. avenae was influenced by artificial diets containing different amounts of gramine (df = 4, 10, F = 58.66, P < 0.001) (Fig. 3 GST). GST activity was significantly greater in S. avenae that fed on the diet containing 0.05, 0.1, and 0.2 mM of gramine than on the control diet. A positive correlation was observed between gramine concentration in diet and GST activity in S. avenae (N = 5; r = 0.940; P = 0.009).
CarE activity in S. avenae was also affected by the increased gramine in the diet (df = 4, 10, F = 150.16, P < 0.001) (Fig. 3 CarE). Gramine concentration was positively correlated with CarE activity in S. avenae (N = 5; r = 0.889; P = 0.022).
POD and PPO activities were greater in S. avenae that fed on the artificial diet containing gramine than those on the control diet (df = 4, 10; F POD = 113.20, F PPO = 57.74, P < 0.001) (Fig. 4 POD, PPO). Activities of both enzymes appeared to peak in S. avenae that fed on the diet containing 0.025 mM gramine. Then, enzymatic activities gradually increased with increased gramine (between 0.05 and 0.2 mM). PPO activity was positively correlated with dietary gramine levels (N = 5; r = 0.903; P = 0.018). However, the correlation between POD activity and dietary gramine concentration was weak (N = 5; r = 0.800; P = 0.052).
With the exception of 0.025 mM gramine treatment, CAT activity in S. avenae was suppressed by higher gramine concentration (between 0.05 and 0.2 mM) (df = 4, 10; F = 160.10; P < 0.001) (Fig. 4 CAT). The correlation between dietary gramine concentration and CAT activity was not significant (N = 5; r = −0.629; P = 0.128).
Discussion
Many plant alkaloids are toxic to insects and are major resources of biological insecticides (Corcuera 1984; Jiang et al. 1999). Gramine has been considered as a deterrent and/or toxicant to many herbivorous insects such as Schizaphis graminum, Rhopalosiphum padi, S. avenae, and Locusta migratoria (Corcuera 1984; Zúñiga and Corcuera 1986; Leszczynski et al. 1989; Kanehisa et al. 1990; Rustamani et al. 1992; Moharramipour et al. 1997; Ishikawa and Kanke 2000; Wang et al. 2006). This study showed that S. avenae mortality caused by exposure to dietary gramine was dosage-dependent with a defined LC50, providing further evidence that gramine is active in plant resistance against aphids.
Detoxification enzymes (i.e., CarE and GST) play an important role in insect counter-resistance to plant secondary metabolites. The activity of these insects is closely related to the level of secondary metablites in host plants. CarE activity varies significantly among the populations of Aphis gossypii collected from different cotton varieties (Gao 1992; Jiang and Guo 1996). A higher CarE activity was observed in R. padi from resistant wheat varieties compared to susceptible varieties (Chen et al. 1997; Cai et al. 2004). Previous studies showed that alkaloids have been used as insecticides to regulate esterase activity in Lipaphis erysimi (Katenbach) and Plutella xylostella (L.) (Luo et al. 1997). The indole alkaloid gramine used in this study increased CarE activity in S. avenae, and the increase was positively correlated with dietary gramine concentrations, suggesting that CarE is involved with gramine detoxification.
GSTs (EC 2.5.1.18) constitute a group of enzymes that are involved in the detoxification of endogenous or exogenous toxic compounds (Vos and van Bladeren 1990). Increased level of GSTs in insects has been associated with resistance to a variety of insecticides (Foumier et al. 1992). Leszczynski et al. (1993) reported that GST activity was higher in S. avenae that fed on resistant wheat cultivars with high concentrations of phenolic compounds than those that fed on the susceptible ones. In this study, increased GST activity in aphids was observed when they fed on diets containing higher gramine concentrations, and enzyme activity was positively correlated with gramine concentration (Fig. 3). These results indicate that GSTs play a positive role in aphid antiresistance against allelochemicals (e.g., phenolics and gramine) in cereals.
POD and PPO are oxidoreductases, and in phytophagous insects, they may be able to counter plant resistance by reducing plant phenolics and their derivatives (Urbanska and Leszczynski 1992; Leszczynski et al. 1993). Phenolic compounds are involved in the resistance of cereal against aphids (Leszczynski et al. 1985, 1996). When aphids fed on a diet containing different concentrations of gramine, significantly different activities of POD and PPO were detected among the concentrations, and the gramine concentrations were correlated strongly with PPO activity in aphids but weakly with POD activity (Fig. 4). These results suggest that both POD and PPO in aphids are involved in gramine metabolism.
CAT is the classical enzyme in aerobic organisms that catalyzes the decomposition of hydrogen peroxide. This enzyme occurs in the midgut of S. avenae (Felton and Duffey 1991; Urbańska 2007). Many plant phenolics enhance the enzymatic activity in S. avenae (Figueroa et al. 1999; Loayza-Muro et al. 2000; Lukasik 2007). Interestingly, the opposite was observed in the present study, as S. avenae CAT activity was strongly reduced by higher gramine concentrations. However, significant correlations were not found between the activity and gramine concentration. This suggests that S. avenae CAT may be dissimilarly modified by the different cereal allelochemicals, i.e., alkaloids vs. phenolics.
In summary, gramine is considered to be an important secondary metablite in host plant resistance. This study showed that dietary gramine was toxic to S. avenae. In response to gramine, S. avenae enhanced CarE and GST activities, as well as PPO and POD activities, thus possibly countering the resistance.
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Acknowledgements
This research was partly supported by the National Basic Research Program from Ministry of Science and Technology of the People’s Republic of China (“973” Program, Grant No. 2006CB100206), Public Welfare Project from Ministry of Agriculture of People’s Republic of China (Grant No. 200803002), National Support Program from Ministry of Science and Technology of People’s Republic of China (Grant No. 2006BAD08A05) and the Initiation Research Program of China Agricultural University (Grant No. 2004050).
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Open Access This is an open access article distributed under the terms of the Creative Commons Attribution Noncommercial License (https://creativecommons.org/licenses/by-nc/2.0), which permits any noncommercial use, distribution, and reproduction in any medium, provided the original author(s) and source are credited.
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Cai, QN., Han, Y., Cao, YZ. et al. Detoxification of Gramine by the Cereal Aphid Sitobion avenae . J Chem Ecol 35, 320–325 (2009). https://doi.org/10.1007/s10886-009-9603-y
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DOI: https://doi.org/10.1007/s10886-009-9603-y