Seeds of mustard (B. juncea L. cv. Ro Agro 4001) were surface sterilized with 0.01% HgCl₂ solution, rinsed with double distilled water and germinated in 23-cm diameter earthen pots filled with acid-washed sand purified according to Hewitt (1966). The plants were raised in full strength modified Hoagland nutrient solution containing 3 mM KNO₃, 2 mM Ca(NO₃)₂, 1 mM NH₄H₃PO₄, 50 μM KCl, 25 μM H₃BO₄, 2 μM MnCl₂, 20 μM ZnSO₄, 0.5 μM CuSO₄, 0.5 μM (NH₄)₆Mo₇O₂₄, and 20 μM Na₂Fe-EDTA, supplied on alternate days. After germination, three healthy plants of nearly equal size in each pot were maintained. The pots were kept in the naturally illuminated green house of the Botany Department, Aligarh Muslim University, Aligarh (India) [average day/night temperatures, 20 ± 3 and 12 ± 2°C, respectively; relative humidity, 60 ± 5%; photosynthetically active radiation (PAR), 750 ± 25 μmol m^-2 s^-1; critical photoperiod, 10–12 h]. Experiments were conducted independently to evaluate the effect of 0, 5, 10, and 20 μM MeJA sprayed on plants at 15 days after sowing (DAS) in presence or absence of 50 μM Cd on content of H₂O₂ and GSH, photosynthesis, and plant dry mass. Based on the results of this experiment, 10 μM MeJA was selected for spraying on plants grown with or without 1.0 mM SO42– and 50 μM Cd to determine the effectiveness of MeJA on S-assimilation and GSH production, and alleviation of Cd stress. The concentration 1.0 mM SO42– was used to initiate S-assimilation and is considered as optimal concentration for mustard (Asgher et al., 2014). Cd concentration used was based on the findings of our previous results (Asgher et al., 2014; Per et al., 2016). To substantiate the role of MeJA-mediated GSH production through S-assimilation in Cd stress alleviation, a GSH biosynthesis inhibitor, BSO (0.5 mM) was added to Cd, MeJA + Cd and MeJA + Cd + S treatments. The effects of the three treatments were compared with the effect of Cd treated plants alone. In experiments, 50 μM Cd or 1.0 mM SO42– treatment was given along with nutrient solution at 10 DAS and observations were recorded at 30 DAS. The source of Cd was CdCl₂. MgSO₄ was used for obtaining 1.0 mM SO42– and Mg²⁺ was maintained in all treatments including control by the addition of appropriate MgCl₂ as described earlier (Nazar et al., 2014). Each pot was supplied with 250 mL nutrient solution. The experiment followed a randomized complete block design and was conducted in four replications.

Leaf samples were dried for 48 h at 80°C in an oven and the dried tissue was weighed, ground to fine powder and digested with concentrated HNO₃/HClO₄ (3:1, v/v). The content of Cd was determined by atomic absorption spectrophotometer (GBC, 932 plus; GBC Scientific Instruments, Braeside, Australia).

The content of H₂O₂ was determined by adopting the method of Okuda et al. (1991) in leaf tissues (0.5 g) grounded in ice-cold 200 mM HClO₄. The sample was centrifuged at 1200 × g for10 min followed by neutralization of HClO₄ of the supernatant with 4 M KOH. The insoluble KClO₄ was eliminated by further centrifugation at 500 × g for 3 min. In a final volume of 1.5 mL, the reaction mixture contained 1 mL of the eluate, 400 μL of 12.5 mM 3-(dimethylamino) benzoic acid in 0.375 M phosphate buffer (pH 6.5), 80 μL of 3-methyl-2-benzothiazoline hydrazone, and 20 μL of peroxidase (0.25 unit). The reaction was started by the addition of peroxidase at 25°C and the increase in absorbance was recorded at 590 nm.

Lipid peroxidation in leaves was determined in terms of the content of TBARS as described by Dhindsa et al. (1981). Fresh leaf tissues (0.5 g) were ground in 0.25% 2-thiobarbituric acid (TBA) in 10% trichloroacetic acid (TCA) using mortar and pestle. After heating at 95°C for 30 min, the mixture was rapidly cooled on ice bath and centrifuged at 10,000 × g for 10 min. To 1 mL of the supernatant, 4 mL 20% TCA containing 0.5% TBA was added. The absorbance of the supernatant was read at 532 nm and corrected for non-specific turbidity by subtracting the absorbance of the same at 600 nm. The content of TBARS was calculated using the extinction coefficient (155 mM^-1 cm^-1).

The method of Lappartient and Touraine (1996) was adopted for the measurement of ATP-sulfurylase (ATP-S) activity. The activity of ATP-S was assayed in vitro in leaves by measuring molybdate-dependent formation of pyrophosphate. Fresh leaf tissues (1.0 g) were ground at 4°C in buffer consisting of 10 mM Na₂ EDTA, 20 mM Tris-HCl (pH 8.0), 2 mM dithiothreitol (DTT), and 0.01 g mL^-1 polyvinylpyrrolidone (PVP), using1:4 (w/v) tissue to buffer ratio. The homogenate was centrifuged at 20,000 × g for 10 min at 4°C. The supernatant was used for in vitro ATP-S assay. The reaction was initiated by adding 0.1 mL of the extract to 0.5 mL of the reaction mixture, which contained 7 mM MgCl₂, 5 mM Na₂MoO₄, 2 mM Na₂ ATP, and 0.032 units mL^-1 of sulfate-free inorganic pyrophosphate in 80 mM Tris-HCl buffer (pH 8.0). Another aliquot from the same extract was added to the reaction mixture but without Na₂MoO₄. Incubations were carried out at 37°C for 15 min, after which phosphate was determined using UV-VIS spectrophotometer (LT-2700, UV/VIS Analytical Technologies Limited, Labtronics, India).

For the determination of S content, dried leaf material (0.1 g) was digested in a mixture of concentrated HNO₃ and 60% strength HClO₄ (85:15, v/v) and total S in plant samples was determined using turbidimetric method (Chesnin and Yien, 1950). Turbidity in 5 mL aliquot was developed by adding 2.5 mL gum acacia (0.25%) solution, 1.0 g BaCl₂ sieved through 40–60 mm mesh and the volume was made to 25 mL with de-ionized water. The contents of 25 mL volumetric flask were thoroughly shaken till BaCl₂ completely dissolved. The values were recorded at 415 nm within 10 min after the turbidity development. A blank was run simultaneously after each set of determination.

Glutathione content was determined following the method of Anderson (1985). Fresh leaves (0.5 g) were homogenized in 2.0 mL of 5% sulphosalicylic acid under cold conditions. The homogenate was centrifuged at 10,000 × g for 10 min. To 0.5 mL of supernatant, 0.6 mL of phosphate buffer (100 mM, pH 7.0) and 40 μL of 5′5′-dithiobis-2-nitrobenzoic acid (DTNB) were added. After 2 min the absorbance was read at 412 nm. The details of the procedure are given in our earlier work (Fatma et al., 2014).

The activity of SOD was determined using the method of Giannopolitis and Ries (1977) and Beyer and Fridovich (1987), while activity of APX and GR was assayed by the Foyer and Halliwell (1976) and Nakano and Asada (1981), respectively, with slight modifications. Fresh leaf tissues (0.2 g) were homogenized in chilled mortar and pestle with an extraction buffer containing 0.05% (v/v) Triton X-100 and 1% (w/v) polyvinylpyrrolidone in 100 mM potassium-phosphate buffer (pH 7.0). At 4°C, the homogenate was centrifuged at 15,000 × g for 20 min. The supernatant obtained after centrifugation was used for the assay of SOD and GR. For the assay of APX extraction buffer was supplemented with 2 mM AsA. The details of procedure have been described earlier in Fatma et al. (2014).

Gas exchange parameters (net photosynthesis, stomatal conductance, and intercellular CO₂ concentration) were measured in fully expanded uppermost leaves of plants using infrared gas analyzer (CID-340, Photosynthesis System, Bio-Science, USA). The measurements were done on a sunny day at light saturating intensity; PAR; 780 μmol m^-2 s^-1 and atmospheric CO₂ concentrations; 370 ± 5 μmol mol^-1.

The activity of ribulose 1,5-bisphosphate carboxylase/oxygenase (Rubisco; EC 4.1.1.39) was determined adopting the method of Usuda (1985) by monitoring NADH oxidation at 30°C at 340 nm. For enzyme extraction, leaf tissue (1.0 g) was homogenized using chilled mortar and pestle with ice-cold extraction buffer containing 0.25 M Tris-HCl (pH 7.8), 0.05 M MgCl₂, 0.0025 M EDTA and 37.5 mg DTT. This homogenate was centrifuged at 4°C at 10,000 × g for 10 min. The resulting supernatant was used to assay the enzyme. The reaction mixture (3 mL) contained 100 mM Tris-HCl (pH 8.0), 40 mM NaHCO₃, 10 mM MgCl₂, 0.2 mM NADH, 4 mM ATP, 5 mM DTT, 1U of glyceraldehyde 3-phosphodehydrogenase, 1 U of 3-phosphoglycerate kinase, and 0.2 mM ribulose 1,5-bisphosphate (RuBP).

Chlorophyll content was measured in the intact leaves with the help of SPAD chlorophyll meter (502 DL PLUS, Spectrum Technologies, USA). Chlorophyll a fluorescence was measured using Junior-PAM chlorophyll fluorometer (Heinz Walz, Germany). Prior to the measurements of fluorescence intensity, leaf sections were dark-adapted for at least 30 min in order to relax the reaction center. Minimal fluorescence (F_o) and maximum fluorescence (F_m) were measured in dark-adapted leaves with a low measuring beam at a light intensity of 125 μmol m^-2 s^-1, whereas under light-adapted condition, minimal fluorescence (F_o′) and maximum fluorescence (F_m′) were measured in the same leaves with a saturating light intensity (780 μmol m^-2 s^-1) together with steady-state fluorescence (F_s). The variable fluorescence (F_v and F_v′) was calculated using the values of F_m-F_o and F_m′-F_o′, and actual PSII efficiency (ΦPSII) was determined as F_m′-F_s/F_m′, maximal efficiency of PSII by using F_v/F_m and intrinsic efficiency of PSII by using F_v′/F_m′. Using fluorescence parameters determined in both the light- and dark-adapted states, the photochemical quenching (qP) and non-photochemical quenching (NPQ) parameters were calculated. qP was calculated as (F_m′-F_s)/F_v′ and NPQ as (F_m-F_m′)/F_m′ (Maxwell and Johnson, 2000). Electron transport rate (ETR) was calculated by the following formula: ΦPSII × photosynthetic photon flux density × 0.5 × 0.84 as suggested by Krall and Edwards (1992).

Leaf tissues for chloroplast ultrastructure were prepared for transmission electron microscopy (TEM) by adopting the method of Sandalio et al. (2001) with slight modifications. Leaf samples were cut with razor blade into 1 mm² segments and fixed in 2.5% glutaraldehyde solution in 50 mM phosphate buffer (pH 6.8) for 2.5 h at room temperature. Leaf tissue was then post-fixed for 30 min in 1% osmium tetroxide in 50 mM sodium cacodylate buffer (pH 7.2) and dehydrated in ethanol graded series (30–100%, v/v). After dehydration in a graded series of ethanol, replaced to propylene oxide, and then the tissue was embedded in Spurr resin. Ultrathin sections were taken by using Leica EM UC6 ultramicrotome. Sections were stained with uranyl acetate and lead citrate and examined using a transmission electron microscope (JEOL 2100F, JAPAN) accelerating voltage at 120 kV and magnification at 6000× and 1200×. The chloroplast ultrastructure (thylakoid membranes) was observed from TEM images.

For measuring growth characteristics, plants were uprooted, washed and dried on blotting paper, and were kept in an oven at 80°C till constant weight. The samples were weighed after drying to obtain dry mass. Leaf area was measured using a leaf area meter (LA211, Systronics, New Delhi, India).

Data were analyzed statistically using analysis of variance (ANOVA) by SPSS 17.0 for Windows, and presented as treatment mean ± SE (n = 4). Least significant difference (LSD) was calculated for the significant data at P < 0.05 and P < 0.01. Bars showing the same letter are not significantly different by LSD test at P < 0.05 or P < 0.01.

In the absence of Cd, 5 and 10 μM MeJA did not influence content of H₂O₂, net photosynthesis and plant dry mass, but 20 μM MeJA significantly increased H₂O₂ content and decreased net photosynthesis and plant dry mass as compared to the control. The GSH content remained unchanged with MeJA concentrations as compared to the control (Table 1). In the presence of Cd, spraying of 10 μM MeJA was more effective than 5 μM MeJA in reducing H₂O₂ content (-31.7%) and increasing GSH content (+52.6%) as compared to the Cd treated plants (Table 1).

Net photosynthesis and plant dry mass were favorably influenced by MeJA treatment under Cd stress. Application of 10 μM MeJA increased net photosynthesis and plant dry mass by about two-times as compared to the Cd treated plants (Table 1).

To determine the role of MeJA in oxidative stress tolerance, we compared the effect of MeJA on oxidative damage induced by Cd. Application of either MeJA or S reduced Cd content about equally by 93% as compared to the Cd treated plants. The combined treatment of MeJA plus S further reduced the Cd content by 156% in comparison with the Cd treated plants (Figure 1).

Plants treated with MeJA or S in the absence of Cd showed that S only could reduce H₂O₂ and TBARS contents and the effect of MeJA did not differ with that of control plants. Plants treated with Cd showed an increase of about more than two-times in TBARS content as compared to the control plants. However, treatment with MeJA or S reduced the content of H₂O₂ and TBARS in Cd stressed plants almost equally by about 60%, and the combined treatment MeJA + S reduced oxidative stress in Cd stressed plants more prominently, by diminishing H₂O₂ and TBARS content by about 70% (Figure 1).

To assess the involvement of antioxidant enzymes in Cd tolerance, activity of SOD, APX, and GR was evaluated under Cd stress. Cd increased the activity of SOD, APX, and GR by 36%, 67%, and 47%, respectively as compared to the control. Application of S in absence of Cd increased activity of antioxidant enzymes, but MeJA application showed no significant changes in the activity of antioxidant enzymes as compared to the control. Plants receiving MeJA or S in the presence of Cd exhibited equal increase in the activity of SOD by about 74%, APX by 140% and GR by 127% as compared to the control. More prominent increase in the activity was found when S was given with MeJA in presence of Cd increasing activity of SOD by 90%, APX by 188% and GR by 173% in comparison with the control (Figure 2).

Under Cd stress, activity of ATP-S increased by 31% and S content decreased by 36% in comparison with the control. Application of S or MeJA plus S increased ATP-S activity equally by about 62% and S content by 26% in comparison with the control under non stress condition. MeJA alone did not produce any significant change in the activity of ATP-S and S content as compared to the control. Plants receiving S or MeJA in the presence of Cd showed increase in the activity of ATP-S by about 52% as compared to the Cd treated plants. In presence of Cd, MeJA together with S increased ATP-S activity by 67% as compared to the Cd treated plants (Figure 3).

Plants grown with Cd showed significant increase in the content of GSH by 21% as compared to the control. Supplementation of S increased GSH by 40% in the absence of Cd, while MeJA alone showed no significant increase in GSH content in comparison with the control. In the presence of Cd, however, MeJA or S effectively increased GSH content equally by about 30% in comparison with the Cd treated plants. The combined application of MeJA and S in the presence of Cd more prominently increased GSH content by 40% in comparison with the Cd treated plants (Figure 3).

Cadmium stress severely affected gas exchange parameters, chlorophyll content and Rubisco activity as compared to the control. The plants receiving S showed higher photosynthesis as compared to the control in the absence/presence of Cd. In the presence of Cd, plants receiving S or MeJA completely alleviated the Cd stress and enhanced photosynthesis as compared to the control. In the absence of Cd, plants receiving S showed increase in net photosynthesis by 40%, stomatal conductance by 19%, intercellular CO₂ concentration by 27% and chlorophyll content by 27% and Rubisco activity by 42% in comparison with the control. However, no significant increase as compared to the control was observed with MeJA application in the absence of Cd. In Cd treated plants, application of MeJA or S was effective in enhancing net photosynthesis by 81 and 102%, stomatal conductance by 32 and 37%, intercellular CO₂ concentration by 36 and 36%, chlorophyll content by 74 and 83%, and Rubisco activity by 84 and 100%, respectively, as compared to the Cd treated plants. The treatment with MeJA and S together showed more pronounced increase in net photosynthesis by 117%, stomatal conductance by 41%, intercellular CO₂ concentration by 53%, chlorophyll content by 95%, and Rubisco activity by 117% as compared to the Cd treated plants (Table 2).

The chlorophyll fluorescence parameters varied under different treatments. Plants grown with Cd exhibited reduced maximum PSII efficiency (-13%), intrinsic PSII efficiency (-25%), actual PSII efficiency (-40%), qP (-45%), and ETR (-40%) as compared to the control. However, NPQ increased with Cd stress by 62% as compared to the control. Application of MeJA or S alone improved the above characteristics equally in Cd treated plants in comparison with the Cd treated plants. Application of MeJA and S together more prominently reversed the effect of Cd on chlorophyll fluorescence parameters and resulted in increase in maximum PSII efficiency, intrinsic PSII efficiency, actual PSII efficiency, qP, and ETR by 30%, 51%, 96%, 98%, and 96%, respectively, and decreased NPQ by 46% in comparison with the Cd treated plants (Figure 4).

The TEM images of ultrastructure of chloroplasts from leaves samples are shown in Figure 5. Under normal conditions, chloroplasts were of regular shape with well arranged thylakoid systems. The analysis of TEM of plants grown with Cd showed disturbances in chloroplast ultrastructure. Chloroplast from Cd-treated plants showed disorganized thylakoid systems, however, plants receiving MeJA plus S in the presence of Cd greatly modified the chloroplast ultrastructure and chloroplast showed regular shape with well arranged thylakoid systems containing a markedly increased number of thylakoid stacks (Figure 5).

Cadmium stress inhibited the development of leaf area and plant dry mass. Application of S increased leaf area by 43% and plant dry mass by 17% in the absence of Cd in comparison with the control. MeJA alone did not prove effective in increasing leaf area and plant dry mass in the absence of Cd. In the presence of Cd, however, MeJA or S increased leaf area equally by about 90% and plant dry mass by about 60%, respectively, as compared to the Cd treated plants. More prominent increase in leaf area and plant dry mass was noted with combined treatments of MeJA and S (Figure 6).

Application of MeJA lowered the impact of Cd on photosynthetic parameters through increase in production of GSH via S-assimilation. These observations were found when comparison of plants treated with Cd or Cd plus BSO was made with plants receiving BSO in presence of MeJA and Cd or MeJA, Cd and S. Supplementation of BSO to plants treated with MeJA in presence of Cd or MeJA in presence of Cd and S resulted in more negative effects on photosynthetic and growth parameters in comparison with the Cd treated plants. Plants raised under these treatments exhibited enhanced H₂O₂ content and lowered GSH content in comparison with the Cd treated plants. However, addition of BSO to Cd treated plants resulted in greatest H₂O₂ content and lowest GSH content with highest decrease in photosynthesis and growth as compared to the other treatments. The plants treated with S in presence of MeJA, Cd, and BSO showed lesser decrease in photosynthesis and growth in comparison with the plants treated with MeJA, Cd, and BSO (Table 3).

The lipid peroxidation and H₂O₂ generation are indicators of oxidative stress and the general outcome of metal toxicity (Srivastava et al., 2014; Khan et al., 2015). Lipid peroxidation and H₂O₂ content significantly increased with the increase of Cd accumulation in Cd treated plants (Figure 1). Addition of MeJA plus S, however, maximally decreased contents of H₂O₂ and TBARS showing the ability of MeJA in alleviation of Cd-induced oxidative stress. These findings are supported by the previous results of Singh and Shah (2014), Hanaka et al. (2015) and Farooq et al. (2016). Plants under oxidative stress induce synthesis of antioxidant metabolites and activity of antioxidant enzymes for protection against oxidative stress. In this study, the application of MeJA and S in Cd-stressed plant increased the activity of antioxidant enzymes more than their individual application (Figure 2) and substantially decreased ROS (Figures 1B,C). Application of 5 μM MeJA in O. sativa (Singh and Shah, 2014), 0.1–1.0 μM MeJA in Capsicum frutescens (Yan et al., 2013), 0.1–10 μM MeJA in Kandelia obovata (Chen et al., 2014), and 0.1 μM MeJA in Solanum nigrum (Yan et al., 2015) has resulted in increased activity of antioxidant enzymes and Cd tolerance. Furthermore, application 0.1–10 μM MeJA minimized oxidative stress in As exposed B. napus plants by enhancing enzymatic activity and gene expression of antioxidant enzymes and also by regulating multiple transcriptional pathways involved in oxidative stress responses (Farooq et al., 2016).

Application of MeJA or/and S increased activity of ATP-S and content of S and GSH under Cd stress (Figure 3). Studies have shown that thiol metabolism and antioxidant defense system increased in Hordeum vulgare plants subjected to metals stress (Astolfi et al., 2012). The results reported here have suggested that ATP-S plays a key role in maintaining GSH pool required for Cd stress tolerance. The potential of plants to survive in Cd contaminated conditions has been found to improve by up-regulation of S-assimilation pathway (Wangeline et al., 2004; Bashir et al., 2013). Under normal conditions, GSH level is maintained in plant cells in a steady state via a low level of transcription, translation, and optimal enzyme activity. However, when plants are subjected to stress, the homeostasis is perturbed and GSH pool is consumed to combat stress. The increased GSH production in the presence of MeJA as observed in the present study in Cd-stressed plant is in close conformity to the results of Singh and Shah (2014) in O. sativa under Cd stress and Farooq et al. (2016) in B. napus under As stress, who found that antioxidant system was stimulated with MeJA. Plants with improved capacity for GSH synthesis have been found to display higher Cd-tolerance (Schützendübel et al., 2002; Yan et al., 2015). Xiang and Oliver (1998) have reported that JA treatment increased the transcript levels of γ-ECS (GHS1) and GSH2 as well as GR and also several GSH-S-transferase encoding genes (Schenk et al., 2000; Sasaki et al., 2001).

The increase in Rubisco activity with MeJA suggests restoration of photosynthetic apparatus in Cd-stressed plants. The role of MeJA in protecting plants under various abiotic stresses is controversial. However, our results have shown that individual or combined application of MeJA and S favored S-assimilation and GSH synthesis. This cumulatively protected chloroplast ultrastructure. Iqbal et al. (2012) have shown the relationship between S allocation in leaves and Rubisco activity. The decreased chlorophyll content in response to Cd supply was related to disorganization in chlorophyll biosynthesis (Parmar et al., 2013). MeJA at 100 μM or higher concentration repressed germination (Kobayashi et al., 2010) and plant growth (Jubany-Marí et al., 2010), Rubisco genes, chlorophyll a/b-binding protein, light harvesting complex II (Jung et al., 2007). In contrast, lower MeJA concentration mostly stimulated plant growth, lateral root initiation, dry matter accumulation, photosynthetic pigment levels, and net photosynthetic rate (Tung et al., 1996; Mabood et al., 2006; Piotrowska et al., 2010; Wu et al., 2012). Our study showed that 10 μM MeJA improved chlorophyll content, gas exchange parameters and Rubisco activity under Cd stress. This was associated with the activation of antioxidant enzymes and recovery of photosynthetic efficiency. Keramat et al. (2010) have also reported that MeJA at 0.01 mM was more effective in reducing the damages of Cd stress on shoot dry weight and total chlorophyll content in G. max. Recently, it has been shown that S and Se increased photosynthesis via increase in the allocation of N and S to Rubisco in B. juncea and Triticum aestivum crops (Fatma et al., 2014; Khan et al., 2015).

The drop in chlorophyll fluorescence under HMs stress results from destruction of antenna pigments by the partial block of electron transport from PSII to PSI (Krupa et al., 1993). The application of MeJA together with S prevented the chloroplast structural damage under Cd stress (Figure 5). It has been suggested that the lipid-to-chlorophyll ratio is a good estimate for the protein-packing density in thylakoid, and the high lipid-to-chlorophyll ratio reflects a low protein-packing density (Kirchhoff, 2013). In the present study, plants receiving MeJA and S exhibited lower level of lipid peroxidation and showed higher chlorophyll content than control or Cd treated plants. A coordinated impact of MeJA and S on the ultrastructural changes of chloroplasts under Cd stress has not been described earlier.

The increase in growth with MeJA or/and S is attributed to GSH-mediated changes in photosynthesis. The maximum alleviation of Cd stress on growth was observed with the combined treatment of MeJA plus S apparently because of more efficient S-assimilation and GSH production that resulted in maximum protection of cell (Figure 6). MeJA treatment has also been reported to reduce the toxic effects of Cd and restored plant growth (Keramat et al., 2009; Kováčik et al., 2011; Yan et al., 2015). Similarly, 0.001 and 0.01 mM MeJA alleviated Cu and Cd ions toxicity on growth in A. thaliana (Maksymiec and Krupa, 2002; Yan et al., 2013).

There was involvement of MeJA in production of GSH through its effect on S-assimilation and protection of photosynthesis under Cd stress. MeJA enhanced S utilization in GSH synthesis under Cd stress, so that the highest GSH content was observed in Cd + S + MeJA treated plants. The same plants showed also the highest ATP-S activity (Figure 3), the lowest Cd content among stressed plants (Figure 1A), and the highest antioxidant response (Figure 2). Application of BSO to plants treated with Cd reduced production of GSH and inhibited photosynthesis, but GSH production and photosynthesis were higher in plants receiving MeJA or MeJA and S under Cd stress (Table 3). This reduction in GSH production aggravated oxidative damage significantly by increasing H₂O₂ production and consequently reduced photosynthesis and growth characteristics. In the presence S, MeJA stimulated GSH production via increased S-assimilation under Cd even with the supplementation of BSO. It has been suggested that MeJA either up-regulated the expression of genes involved in biosynthesis of GSH or facilitated the synthesis of GSH (Xiang and Oliver, 1998; Farooq et al., 2016) and enhanced peroxide removal and eventually photosynthetic efficiency under Cd stress. Therefore, MeJA-mediated protection of photosynthesis under Cd stress was correlative with GSH production.