Susceptibility and activity of glutathione S-transferases in nine field populations of Panonychus citri (Acari: Tetranychidae) to pyridaben and azocyclotin.
The METI acaricides (i.e., tebufenpyrad, fenpyroximate, pyridaben, and fenazaquin), which are now widely used globally, were developed in the 1990s and inhibit complex I (NADH: ubiquinone oxidoreductase) of the mitochondrial respiratory pathway (Hollingworth & Ahammadsahib 1995). Pyridaben (2-tert-butyl-5-(4-tert-butyl-benzoylthio)-4-chloropyridazin-3(2H)-one) is a pyridazinone-derived acaricide that functions by binding its active site to a crucial co-enzyme in mitochondria (complex I at coenzyme site Q), and thus inhibits electron transport in phytophagous mites and insects (Denholm et al. 1998; Hirata et al. 1995). However, azocyclotin is an organotin miticide whose mode of action is to disrupt ATP formation by inhibiting oxidative phosphorylation (Van Leeuwen et al. 2010).
Pyridaben was introduced in China in 1992 and has been widely used in ornamentals and orchards to control mite pests resistant to conventional acaricides (Shi & Feng 2006). According to the Institute of the Control of Agrochemicals, Ministry of Agriculture, P. R. China (ICAMA), 346 commercial products of pyridaben were registered for use against P. citri. Compared to pyridaben, commercial products of other METI acaricides registered in China between 2008 and 2010 were 2 products containing fenazaquin and 44 products containing fenpyroximate, (ICAMA 2010). However, several field populations of P. citri have already developed high levels of pyridaben resistance in spite of its short term use. Recent investigation has demonstrated that the populations collected from the Chongqing municipality, Pinghe in Fujian Province, Linhai in Zhejiang province, and Yidu in Hubei province have expressed 163.3-, 266.5-, 417.9-, and 601.5-fold resistance to pyridaben, respectively (Hu et al. 2010). Judging by the present status, effort needs to be placed on resistance management to ensure future effective pest control. In addition, better understanding of mechanisms of resistance to pyridaben in P. citri is needed for logical selection of alternate acaricides for resistance management.
Glutathione S-transferases (GSTs, EC 188.8.131.52) belong to a supergene family of enzymes that are involved in phase II detoxification of xenobiotics, protection from oxidative damage, and intracellular transport of hormones, endogenous metabolites, and exogenous chemicals (Freitas et al. 2007; Huang et al. 1998). In insects, GSTs have been implicated as a major detoxification mechanism for several classes of insecticides i.e., organophosphates, pyrethroids, carbamates, and chlorinated hydrocarbons such as DDT (Lumjuan et al. 2005; Willoughby et al. 2007; Zhu et al. 2007). However, elevated levels of GSTs activity have been shown recently to be associated with the resistance of spider mite to acaricides, particularly in abamectin resistant populations of T. urticae (Konanz & Nauen 2004). Furthermore, experiments with synergists suggest that GSTs have a major role in pyridaben resistance in P. citri (Liu et al. 2010; Meng et al. 2000).
In the present study, 9 field collected populations of P. citri from China were investigated. Preliminary susceptibility screening of the commercially important acaricide pyridaben and a potential alternate acaricide, azocyclotin, was conducted. In addition, comparison analyses of the GSTs from the 9 populations were performed (including the activities, the kinetics, and an in vitro assay), in order to better understand possible mechanisms of pyridaben resistance in field populations of P. citri.
MATERIALS AND METHODS
In 2010, P. citri were collected from citrus orchards in 9 locations in Sichuan Province and Chongqing municipality, China (Table l). In each sample location, more than 2,000 mites with associated citrus leaves were collected from more than 10 citrus trees (Table l). Fresh leaves, collected at random from Citrus reticulata Blanco mandarin orange trees with no prior pesticide exposure from orchards at the Citrus Research Institute, Chinese Academy of Agricultural Sciences, were used to rear the collected mites in the laboratory during the experiments. The leaves were replaced every 3 d. Sites were selected based on their importance as citrus production areas, and they received various levels of acaricide applications for the management of P. citri (Liu et al. 2010). The identity of P. citri was confirmed by J. J. Wang. Voucher specimens (50 for each population) were deposited in the insect collection of Southwest University, Chongqing, China.
Formulated acaricides used in this study were pyridaben 150 g L-1 EC (Saomanjing[R]) and azocyclotin 200 g L-1 SC (Sanzuoxi[R]), which were purchased from Jiangsu Kesheng Group Co., Jiangsu, China, and Jiangxi Huxing Chemical Co., Jiangxi, China, respectively. Bovine serum albumin (BSA), coomassie brilliant blue G-250, and l-chloro-2, 4-dinitrobenzene (CDNB) were supplied by Shanghai Chem. Ltd., Shanghai, China. Reduced glutathione (GSH) and Ethacrynic acid (EA) were purchased from Sigma (St. Louis, Missouri, USA).
In general the bioassay procedures recommended by the Food and Agriculture Organization of the United Nations were followed (FAO 1980). Each field population was assayed by a slide-dip method with 7 treatment concentrations of each acaricide. Each acaricide was diluted with double-distilled water (dd[H.sub.2]O) and various concentrations were tested until a satisfactory range (10-90% mortality) was ascertained. The control group was treated with dd[H.sub.2]O alone. Each slide, containing 30-40 adult female individuals that were 3-5 d old, was dipped into the pesticide solution for 5 s. The slides were placed in an incubator at 28 [+ or -] 1[degrees]C, 75-80% relative humidity, with a photoperiod of light: dark, 14:10 h. Mortality was assessed after 24 h. Mites that did not move after stimulation by a camel hair brush were scored as dead. Each treatment (comprising 3 slides) was replicated 3 times on 3 different days. Mortality data was corrected by Abbott's Formula (Abbott 1925) and analyzed by probit analysis to determine the lethal concentrations ([LC.sub.50]) (Raymond 1985).
One hundred female adults from each population were homogenized in 4 mL ice-cold sodium phosphate buffer (0.02M; pH 7.3) and centrifuged at 5,000 g for 5 min at 4[degrees]C in a CF16RX refrigerated centrifuge (Hitachi Ltd, Tokyo, Japan). The pellets were discarded and the supernatant was again centrifuged at 4[degrees]C for 15 min at 17,500g. Finally, the supernatant was used as the enzyme source for GST activity assays. The protein contents of enzyme homogenates were determined according to the Bradford method with BSA as a standard (Bradford 1976). The measurement was performed with the A-5002 thermomax kinetic microplate reader (Tecan Ltd., Salzburg, Austria) at 595 nm.
Determination of GSTs Activities and Kinetics
GSTs activity was determined with CDNB and GSH as substrates in 96-well microplates (Habig et al. 1974). The total reaction volume per well of a 96-well microplate was 300 [micro]L. This consisted of 100 [micro]L supernatant, 100 [micro]L CDNB (containing 2% [v/v] ethanol) and 100 [micro]L GSH in 0.05 M, pH 7.5 Tris-HCl, with a final concentration of 0.6 mM of CDNB and 6.0 mM and GSH. The non-enzymatic reaction of CDNB with GSH measured without homogenate served as the control. The change in absorbance was measured continuously for 5 min at 340 nm and 37[degrees]C in an A-5002 thermomax kinetic microplate reader (Tecan Ltd., Salzburg, Austria). Changes in absorbance per minute were converted into nmol CDNB conjugated/min/mg protein based on the extinction coefficient of the resulting 2, 4-dinitrophenyl-glutathione ([[epsilon].sub.340nm] = 9.6 [mM.sup.-1] [cm.sup.-1]) (Habig et al. 1974).
The values of [V.sub.max] and [K.sub.m] of total GSTs from P. citri were determined for CDNB and GSH. The activity was recorded as a range of concentrations (0.02-0.6 mM for CDNB or 0.3-6.0 mM for GSH), while the concentrations of the other substrates were kept constant at 6.0 mM GSH or 0.6 mM CDNB. [V.sub.max] and [K.sub.m] values were calculated by the Michaelis-Menten equation in SPSS 10.0 for Windows (Rauch & Nauen 2004).
In vitro Assay
To evaluate the sensitivity of GSTs to different inhibitors, 3 chemicals (pyridaben, azocyclotin, and EA) were selected to assess in vitro inhibition against GSTs. Stock solutions of the inhibitors were diluted with 0.05 M, pH 8.0, Tris-HCl buffer. Twenty-five [micro]L of the enzyme source and 25 [micro]L inhibitor solutions, with an appropriate concentration range (i.e., 1.0-1,000 mg/L for EA, 0.48-384.70 mg/L for pyridaben, and 0.86-1,713.00 mg/L for azocyclotin (which were ascertained from various concentrations of each inhibitor to test the inhibition rate until concentrations causing 10-90% inhibition were delimited), were incubated for 5 min at 37[degrees]C and added to the CDNB/GSH substrate mixture as described above. Reactions without the inhibitor were included as controls. The median inhibition concentration ([I.sub.50]) for each inhibitor was determined based on the log-concentration vs. probit (% inhibition) regression analysis. Three replications were conducted for each treatment above.
All the data from the 9 field populations of P. citri were analyzed by analysis of variance (ANOVA), the means were separated by Duncan's Multiple Range Test or LSD Test for significance (P = 0.05) with SPSS 10.0 for Windows (SPSS 1999). Regression analysis was performed to calculate the GST kinetic parameters, [LC.sub.50] values of different acaricides, and [I.sub.50] values of different inhibitors. The significant level of resistance rate (RR) was ascertained by the confidence interval overlap of the [LC.sub.50] values. The Chi-square goodness-of-fit test was used to determine the difference between the theoretic and the measured values of acaricide toxicity results. Correlation analyses were conducted to find the relationship between GSTs activity and [LC.sub.50] values of each acaricide against the 9 populations of P. citri.
Compared with the reference dose of each acaricide, the Jiangjin and Meishan populations were susceptible to pyridaben and azocyclotin, respectively. In addition, the population sampled from Jiangjin expressed the greatest sensitivity to pyridaben and thus was regarded as relatively susceptible to pyridaben compared to the other 8 populations. Comparison among resistance ratios (RR) with the relatively pyridaben-susceptible population indicated that all other 8 field collected populations had significant levels of resistance. Resistance ratios ranged from 2 (Jianyang population) to 140 (Pujiang population) (Table 2).
The Meishan population had the lowest [LC.sub.50] value when treated with azocyclotin and was used as the relatively susceptible population to azocyclotin for comparison to the other 8 populations. Comparison of RR values to the relatively azocyclotin susceptible population suggested that only the Beibei, Jiangjin, Jintang, Wanzhou, and Zhongxian populations had significant levels of resistance. Resistance ratios ranged from 2 (Jianyang, Pengshan, Pujiang, and Wanzhou populations) to 36 (Beibei population) (Table 2).
Activity of GSTs
The Pujiang population exhibited 4.7-fold increased GST activity in comparison with the pyridaben susceptible population (Jiangjin population), and GST activity in the Beibei, Jintang, Meishan, Pengshan, Wanzhou, and Zhongxian populations was increased 2.3-,1.9-, 1.8-, 2.1-, 2.2-, and 2.7-fold, respectively, in comparison with the Jiangjin population. GST activity in the Jianyang population was 0.9-fold lower than in the Jiangjin population (Fig. l). In addition, the correlation coefficient between GST activity and [LC.sub.50] of pyridaben was r = 0.93, while the correlation coefficient between GST activity and [LC.sub.50] of azocyclotin was r = 0.03 (Fig. 2).
Kinetic Parameters of GSTs
The kinetic parameters of GSTs in P. citri were determined from Lineweaver-Burk plots and presented in Table 3. For the catalytic activity of GSTs toward GSH and CDNB as expressed by the [V.sub.max] value, the Pujiang population had the highest [V.sub.max] value and exhibited a 276.0-fold increased catalytic activity of GSH in comparison with the susceptible Jiangjin population. The catalytic activity of GSH in Jintang, Pengshan, and Zhongxian was increased (8.8-, 2.5-, and 19.0-fold, respectively) compared with the susceptible Jiangjin population. The catalytic activity of GSH in the Beibei, Jianyang, Meishan, and Wanzhou populations decreased compared with the susceptible Jiangjin population. In addition, the catalytic activities of CDNB in the Beibei, Jintang, Pengshan, Wanzhou, and Zhongxian populations were significantly higher than the pyridaben susceptible population, and exhibited 2.5-, 11.6-, 7.0-, 5.1-, and 6.4-fold increases, respectively. However, the catalytic activity of CDNB in the Jianyang, Meishan, and Pujiang populations was 0.7-, 0.1- and 0.3-fold lower, respectively, than that of the pyridaben susceptible population; but no significant difference of catalytic activity of CDNB was detected among these populations (P < 0.05) (Table 3).
[FIGURE 1 OMITTED]
All field collected populations had higher [K.sub.m] values of GSH compared to the reference [K.sub.m] value in the pyridaben susceptible population. Among these, the Pengshan population exhibited a 4.1fold increase in [K.sub.m] value. In addition, the [K.sub.m] value of CDNB in the Jintang, Meishan, Pengshan, Wanzhou, and Zhongxian populations suggested 2.3-, 1.3-, 10.2-, 5.4-, and 2.9-fold increases, respectively, compared with the pyridaben susceptible population. However, the Pujiang population was determined as having the smallest [K.sub.m] value toward CDNB, while the Pengshan population was determined as having the largest [K.sub.m] value toward CDNB among all the populations (Table 3).
In vitro assay
The median inhibition concentrations ([I.sub.50]s) of the 3 inhibitors (EA, pyridaben, and azocyclotin) were calculated for GSTs from the 9 field collected populations of P. citri (Table 4). The statistical analysis indicated that azocyclotin was the most sensitive inhibitor of the GSTs ([I.sub.50] values ranging from 0.00 to 0.52 mg [liter.sup.-1]) compared with the [I.sub.50] values of EA and pyridaben, which ranged between 0.03 to 3.60 and 0.03 to 28.94 mg [liter.sup.-1], respectively.
Panonychus citri presents a challenge to pest managers due to its inherent ability to develop resistance in a few generations. In recent years, some conventional control options for citrus red mite have become restricted, because the use of more toxic compounds, such as dicofol, has been strictly prohibited. Some novel acaricides, such as METIs and spirodiclofen, have been introduced recently. However, after several years of effective use in citrus, resistance problems have arisen. In some citrus growing areas, growers use these novel acaricides more than 5 times per growing season while the label guidelines specify only 2 applications per year (Hu et al. 2010). Development of resistance in citrus red mite can increase grower costs by more than two-fold and theses can mount further as resistance levels escalate. In the current study, the susceptibilities of 9 field collected populations of P. citri to the acaricides, pyridaben, and azocyclotin, were determined. Mites from the Pengshan, Pujiang, Wanzhou, and Zhongxian populations exhibited >10-fold resistance to pyridaben compared with the pyridabensusceptible population collected in Jiangjin. However, with the exception of the Zhongxian population, the preceding populations also had the lowest resistance ratio (<5) for azocyclotin compared with the azocyclotin-susceptible population collected in Meishan. Therefore, azocyclotin may be an effective alternative to manage resistance to pyridaben. Previous studies with a field-collected population of P. citri selected with pyridaben for 12 generations showed that it had developed 35-fold resistance, while it still exhibited a low level of cross-resistance (4-fold) to azocyclotin (Meng et al. 2000). A similar low level of cross resistance to azocyclotin also was found in T. urticae. A pyridaben-resistant colony, maintained in the laboratory, was established by treatment with pyridaben for 20 generations (PR-20 population); and it was extremely resistant to pyridaben (resistance ratio = 240), but showed low levels of resistance (resistance ratio = 3.8) to azocyclotin (Kim et al. 2006). Pyridaben belongs to the METI-acaricides, and cross-resistance between METIs has been reported both in laboratory-selected populations and in field-collected populations of T. urticae (Kim et al. 2006; Stumpf & Nauen 2001). The responses of [F.sub.2] females from the reciprocal crosses of resistant and susceptible individuals suggest that resistance to pyridaben is under monogenic control (Van Pottelberge et al. 2009b). Monogenic resistance, which is considered more likely to spread within populations than polygenic resistance, tends to be more stable and is less easily managed (Roush & McKenzie 1987). Based on the different modes of action between pyridaben and azocyclotin, azocyclotin may be a good rotation acaricide for the management of pyridaben resistance.
[FIGURE 2 OMITTED]
The mechanisms of resistance to acaricides in mite species are reduced penetration, enhanced metabolism, and target site insensitivity. Of these factors, enhanced metabolic detoxification by GSTs, mixed function oxidases (MFOs), and/or esterases (ESTs) has been considered as a main mechanism of acaricide resistance of mites (Van Nieuwenhuyse et al. 2009; Van Pottelberge et al. 2009a). Experiments with synergists (DEM, PBO, and TPP inhibitors against GSTs, MFO, and EST, respectively) suggest that GSTs play a major role in pyridaben resistance in field collected pyridaben-resistant P. citri populations (Liu et al. 2010), while the same result was also reported in a laboratory pyridaben-selected population of P. citri (Meng et al. 2000). However, an experiment with synergists involving the PR-20 population of T. urticae (a field collected population that was further selected with pyridaben for 20 generations) revealed that MFO plays a major role in pyridaben resistance in this population (Kim et al. 2006). We suggest that the different results from the synergist experiments between P. citri and T. urticae might be caused by differences in inter-specific and non-specialized synergistic activity (Young et al. 2005). In the present study, the activity of GSTs from 9 field collected citrus red mites increased as the pyridaben resistance levels increased (Pujiang > Zhongxian > Wanzhou > Pengshan > Beibei > Jintang > Meishan > Jianyang > Jiangjin) with the exception of the Beibei and Jianyang populations. The analysis showed that the correlation coefficient between GSTs activities and the [LC.sub.50] of pyridaben was r = 0.93, while the correlation between GSTs activities and the [LC.sub.50] of azocyclotin was only r = 0.03 (Fig. 2). This could mean that in P. citri field populations GSTs were involved in resistance of to pyridaben but not to azocyclotin.
All the kinetic parameters (including [V.sub.max] and [K.sub.m] for both GSH and CDNB) in the Jintang, Pengshan, and Zhongxian populations increased significantly compared with the pyridaben susceptible population from Jiangjin. In addition, the catalytic activity of CDNB (presented by [V.sub.max]) in the Beibei, Jintang, Pengshan, Wanzhou, and Zhongxian populations were found to be significantly greater than the pyridaben susceptible population (2.5-,11.6-, 7.0-, 5.1-, and 6.4-fold increase, respectively), indicating an over-expression (Konanz & Nauen 2004) or structural alteration (Wang et al. 2008) of GSTs in these populations. The [K.sub.m] value of GSH in all field collected populations increased relative to the [K.sub.m] value in the pyridaben susceptible population. In addition, the [K.sub.m] values of CDNB in the Jintang, Meishan, Pengshan, Wanzhou, and Zhongxian populations was 2.3-, 1.3-, 10.2-, 5.4-, and 2.9-fold, respectively, greater than the [K.sub.m] value of the pyridaben susceptible population.
Ethacrynic acid (EA) always presents a strong inhibitory effect on GSTs in many pests, i.e., Blattella germanica (L.) (Blattellidae) (Yu & Huang
2000), T. urticae (Konanz & Nauen 2004), and Li poscelis paeta (Pearman) (Liposcelididae) (Wu et al. 2009). In our current study, azocyclotin had the greatest inhibitory effect on GSTs compared with EA and pyridaben, indicating that azocyclotin could be used as an effective pesticide synergist for the control of pesticide resistance caused by GSTs, i.e., azocyclotin could block GST activity due to rapid depletion of GSH (Li et al. 2009). Nevertheless, the effectiveness of azocyclotin as a synergist requires further research.
In summary, the present study has provided some basic information on the toxicity of pyridaben and azocyclotin against P. citri, and certain characteristics of GST activity in 9 field populations of P. citri were described. In addition, our study illustrated that GSTs could be associated with varying susceptibility levels to pyridaben. This is only the first step in the biochemical differentiation of various P. citri field populations. The results of further studies will contribute to the understanding of the mechanisms of acaricide resistance in P. citri.
We thank Dr. Helen Hull-Sanders and Stephen Sanders for invaluable comments and improvement of both content and English language. This study was supported in part by a grant from MOA (201103020), the Program for Changjiang Scholars and Innovative Research Team at the University (IRT0976), Natural Science Foundation of Chongqing (CSTC, 2009BA1042), and the earmarked fund for the Modern Agro-industry (Citrus) Technology Research System of China to JinJun Wang. The technical assistance of Yi Yin and Rui Zhang is appreciated.
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JIN-ZHI NIU (1), GUO-YING LIU (2), WEI DOU (1) AND JIN-JUN WANG (1)
(1) Key Laboratory of Entomology and Pest Control Engineering, College of Plant Protection, Southwest University, Chongqing 400716, P.R. China
(2) Sichuan Entry-Exit Inspection and Quarantine Bureau, Chengdu 610041, P.R. China
TABLE L. LOCATIONS, ORIGIN AND YEAR OF SAMPLING OF CHINESE P. CITRI POPULATIONS. Population Location Origin Beibei Chongqing municipality Citrus reticulate Banco Jiangjin Chongqing municipality Citrus reticulate Banco Wanzhou Chongqing municipality Citrus reticulate Banco Zhongxian Chongqing municipality Citrus reticulate Banco Jintang Sichuan Province Citrus reticulate Banco Jianyang Sichuan Province Citrus reticulate Banco Pengshan Sichuan Province Citrus reticulate Banco Pujiang Sichuan Province Citrus reticulate Banco Meishan Sichuan Province Citrus reticulate Banco Population Collection date Beibei 4-16-2010 Jiangjin 5-03-2010 Wanzhou 5-11-2010 Zhongxian 5-19-2010 Jintang 5-21-2010 Jianyang 5-14-2010 Pengshan 5-16-2010 Pujiang 5-29-2010 Meishan 4-11-2010 TABLE 2. SUSCEPTIBILITIES OF 9 FIELD-COLLECTED POPULATIONS OF P. CITRI TO PYRIDABEN AND AZOCYCLOTIN. Acaricide Population n [chi Slope ([+ or -] SE) square] (a) Pyridaben Jiangjin 616 1.33 1.12 ([+ or -] 0.17) Beibei 710 2.11 0.52 ([+ or -] 0.11) Jianyang 687 4.68 0.89 ([+ or -] 0.13) Jintang 485 3.71 0.61 ([+ or -] 0.13) Meishan 575 2.18 0.63 ([+ or -] 0.12) Pengshan 473 0.23 0.93 ([+ or -] 0.18) Pujiang 527 2.00 1.57 ([+ or -] 0.33) Wanzhou 519 0.99 0.75 ([+ or -] 0.16) Zhongxian 670 2.08 1.22 ([+ or -] 0.17) Azocyclotin Meishan 470 5.48 0.31 ([+ or -] 0.08) Beibei 566 2.06 0.63 ([+ or -] 0.10) Jiangjin 515 5.29 1.00 ([+ or -] 0.15) Jintang 688 4.03 0.45 ([+ or -] 0.15) Jianyang 639 5.86 0.61 ([+ or -] 0.12) Pengshan 507 5.50 0.71 ([+ or -] 0.12) Pujiang 519 3.76 0.80 ([+ or -] 0.13) Wanzhou 498 4.07 0.70 ([+ or -] 0.09) Zhongxian 621 3.39 0.46 ([+ or -] 0.10) Acaricide Population [LC.sub.50] [95%CI] RR [95%CI] (mg [liter.sup.-1]) Pyridaben Jiangjin 0.2 [0.2; 0.3] -- Beibei 2.0 [1.1; 3.1] 9 [6; 11] Jianyang 0.5 [0.3; 0.6] 2 [2; 2] Jintang 1.7 [1.0; 3.0] 8 [6; 10] Meishan 1.1 [0.7; 1.4] 5 [4; 5] Pengshan 2.6 [1.6; 4.0] 12 [9; 14] Pujiang 30.9 [23.0; 55.1] 140 [134; 192] Wanzhou 5.3 [3.8; 7.8] 24 [22; 27] Zhongxian 14.9 [11.7; 20.6] 68 [68; 71] Azocyclotin Meishan 40 [21; 70] -- Beibei 1463 [1063; 1656] 36 [30; 37] Jiangjin 128 [72; 206] 3 [2; 5] Jintang 304 [239; 337] 8 [7; 8] Jianyang 88 [(50; 139) 2 [l; 3] Pengshan 87 [53; 154] 2 [l; 3] Pujiang 60 [32; 93] 2 [l; 2] Wanzhou 104 [71; 157] 2 [2; 4] Zhongxian 734 [683; 1115] 18 [17;25] Note: n = number of mites; RR = resistance ratio; CI = confidence interval. (a) Chi-squared goodness-of-fit test. TABLE 3. APPARENT KINETIC PARAMETERS OF GLUTATHIONE S-TRANSFERASES TOWARDS GSH AND CDNB IN THE 9 FIELD-COLLECTED POPULATIONS OF P. CITRI. GSH Population [V.sub.max] [K.sub.m] Jiangjin 311 [+ or -] 11 a 87 [+ or -] 11 a Jianyang 264 [+ or -] 64 a 87 [+ or -] 2 a Meishan 11 [+ or -] 0 a 328 [+ or -] 12 cd Jintang 2744 [+ or -] 178 a 306 [+ or -] 15 c Beibei 194 [+ or -] 53 a 190 [+ or -] 59 b Pengshan 776 [+ or -] 148 a 359 [+ or -] 14 d Wanzhou 11 [+ or -] 1 a 343 [+ or -] 25 cd Zhongxian 5907 [+ or -] 276 a 318 [+ or -] 25 cd Pujiang 85841 [+ or -] 10084 b 120 [+ or -] 7 a CDNB Population [V.sub.max] [K.sub.m] Jiangjin 210 [+ or -] 10 a 58 [+ or -] 14 bc Jianyang 153 [+ or -] 25 a 12 [+ or -] 2 a Meishan 16 [+ or -] 1 a 73 [+ or -] 10 c Jintang 2427 [+ or -] 36 f 134 [+ or -] 18 d Beibei 527 [+ or -] 37 b 33 [+ or -] 2 ab Pengshan 1484 [+ or -] 393 d 593 [+ or -] 56 f Wanzhou 1088 [+ or -] 26 c 316 [+ or -] 14 e Zhongxian 1334 [+ or -] 280 cd 167 [+ or -] 11 d Pujiang 68 [+ or -] 4 a 5 [+ or -] 0 a Each value represents the mean ([+ or -] SE). Mean values within the same column followed by different letters are significantly different in ANOVA (LSD, P < 0.05). [V.sub.max]: nmol [min.sup.-1] [(mg pro).sup.-1]. [K.sub.m]: [micro]M. TABLE 4. [I.sub.50] VALUES OF IN VITRO INHIBITION OF GLUTATHIONE S-TRANSFERASES FROM 9 FIELD-COLLECTED POPULATIONS OF P. CITRI. [I.sub.50] Population EA Pyridaben Jiangjin 0.03 [+ or -] 0.00 a 3.21 [+ or -] 0.53 a Jianyang 0.37 [+ or -] 0.00 b 10.26 [+ or -] 0.00 b Meishan 0.83 [+ or -] 0.20 c 27.21 [+ or -] 2.38 e Jintang 3.60 [+ or -] 0.45 e 12.72 [+ or -] 4.41 c Beibei 1.16 [+ or -] 0.02 d 17.55 [+ or -] 0.74 cd Pengshan 0.06 [+ or -] 0.00 a 24.21 [+ or -] 2.52 de Wanzhou 0.98 [+ or -] 0.03 cd 28.94 [+ or -] 9.17 e Zhongxian 0.24 [+ or -] 0.00 ab 18.40 [+ or -] 3.28 bcd Pujiang 1.09 [+ or -] 0.02 cd 0.03 [+ or -] 0.01 a [I.sub.50] Population Azocyclotin Jiangjin 0.03 [+ or -] 0.00 a Jianyang 0.52 [+ or -] 0.18 c Meishan 0.32 [+ or -] 0.16 b Jintang 0.00 [+ or -] 0.00 a Beibei 0.08 [+ or -] 0.01 a Pengshan 0.02 [+ or -] 0.00 a Wanzhou 0.49 [+ or -] 0.00 c Zhongxian 0.01 [+ or -] 0.00 a Pujiang 0.00 [+ or -] 0.00 a Inhibition measured as 50% inhibitory concentration (i.e., [I.sub.50]) in mg [liter.sup.-1]. Each value represents the mean ([+ or -] SE). Mean values within the same column followed by different letters are significantly different in ANOVA (LSD, P < 0.05).
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|Author:||Niu, Jin-Zhi; Liu, Guo-Ying; Dou, Wei; Wang, Jin-Jun|
|Date:||Jun 1, 2011|
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