Potential of biosynthesized silver nanoparticles using Stenotrophomonas sp. BHU-S7 (MTCC 5978) for management of soil-borne and foliar phytopathogens

Stenotrophomonas sp. is emerging as a popular microbe of global concern with various potential ecological roles. Biosynthesis of gold and silver nanoparticles (AgNPs) using this bacterial strain has shown promising applications in life sciences. However, there is no report on efficient agricultural applications of biosynthesized AgNPs using Stenotrophomonas sp. In this regard, successful biosynthesis of AgNPs using Stenotrophomonas sp. BHU-S7 (MTCC 5978) was monitored by Uv-visible spectrum showing surface plasmon resonance (SPR) peak at 440 nm. The biosynthesized AgNPs were spherical with an average mean size of ~12 nm. The antifungal efficacy of biosynthesized AgNPs against foliar and soil-borne phytopathogens was observed. The inhibitory impact of AgNPs (2, 4, 10 μg/ml) on conidial germination was recorded under in vitro conditions. Interestingly, sclerotia of Sclerotium rolfsii exposed to AgNPs failed to germinate on PDA medium and in soil system. Moreover, AgNPs treatment successfully managed collar rot of chickpea caused by S. rolfsii under greenhouse conditions. The reduced sclerotia germination, phenolic acids induction, altered lignification and H2O2 production was observed to be the probable mechanisms providing protection to chickpea against S. rolfsii. Our data revealed that AgNPs treated plants are better equipped to cope with pathogen challenge pointing towards their robust applications in plant disease management.

at accelerating voltage of 20 kV and 200 kV respectively. The Fourier transform infrared (FTIR) spectrum for analyzing functional nature of AgNPs was recorded on Perkin Elmer FT-IR spectrometer Spectrum Two (Perkin Elmer Life and Analytical Sciences, CT, USA) using potassium bromide (KBr) pellets in the ratio of 1:100. The spectrum was recorded in the diffuse reflectance mode at a resolution of 4 cm −1 in the range of 400-4000 cm −1 wavenumber 42 . For elemental composition, energy dispersive X-ray (EDAX) spectrum was collected using EDAX detector (Oxford Instruments INCAx-sight EDAX spectrometer) equipped with SEM. Furthermore, the thermogravimetric analysis (TGA) was conducted using Pyris1 thermogravimetric analyzer (TGA; Perkin Elmer Life and Analytical Sciences, CT, USA) in order to check thermal stability of biosynthesized AgNPs. For this, sample was subjected to temperature range of 50-700 °C at a heating rate of 10 °C/min under nitrogen atmosphere.
In vitro assay for antifungal activity of biosynthesized AgNPs. The antifungal activity of biosynthesized AgNPs was checked against foliar (Alternaria alternata, Curvularia lunata and Bipolaris sorokiniana) and soil borne (Sclerotium rolfsii) phytopathogens. In case of foliar pathogens, a cavity slide method was used as described by Mishra et al. 24 . For this, conidial suspension was harvested in sterile distilled water from pure and freshly grown culture of A. alternata, C. lunata and B. sorokiniana on Potato Dextrose Agar (PDA) media under aseptic condition. Three experimental sets i.e. control, AgNO 3 control and AgNPs treated sets were prepared in triplicate for each test fungus. In treated set, the conidial suspension was mixed with 2, 4 and 10 μ g/ml of AgNPs and filled in cavity slide. On other side, the control set was maintained by filling the cavity with conidial suspension alone while AgNO 3 control was maintained by mixing 2, 4 and 10 μ g/ml of AgNO 3 with conidial suspension. The cavity slides from all sets were kept carefully inside the petriplate containing sterilized moist blotting paper. These moist chambers containing cavity slides were incubated at 25 ± 2 °C for 24 h. The slides were examined under light microscope (Nikon DS-fi1, Japan) to observe the inhibitory effect of AgNPs on conidial germination.
Further, inhibitory effect of biosynthesized AgNPs on sclerotia germination of Sclerotium rolfsii was investigated by dipping the sclerotia in direct suspension of AgNPs for 12 and 24 h. Later sclerotia were kept on PDA plates for their germination. Sclerotia dipped in sterile distilled water served as control. For more accuracy, sclerotia germination was also checked in soil. For this, control and AgNPs treated sets were prepared in triplicate by placing 25 g garden soil in petriplate. The sclerotia was placed into the soil and drenched with AgNPs suspension maintaining 16% moisture while in control set, soil was drenched with water only. Petriplates were kept in BOD incubator at 25 ± 2 °C for a week.

Tripartite interaction among Cicer arietinum, Sclerotium rolfsii and antifungal biosynthesized
AgNPs under Greenhouse conditions. The antifungal efficacy of biosynthesized AgNPs was evaluated against collar rot disease caused by S. rolfsii (SR) under greenhouse conditions using chickpea (cv. Avrodhi) as a host plant. For conducting greenhouse experiment, plastic pots (5 inch length, 13 cm diameter) were filled with soil (650 g) and 5 chickpea seeds were sown in each pot. For proper seed germination and plant growth, pots were watered to maintain adequate soil moisture. After 15 days of plant growth, following treatments were maintained: (i) unchallenged control (C), (ii) pathogen challenged control (SR control) and (iii) pathogen challenged + AgNPs (SR + AgNPs). Six replicates for each treatment were maintained. The pathogen (S. rolfsii) was introduced to the plants by placing one sclerotium adjacent to the collar region of chickpea in each replicate and further covered with moist cotton for maintaining the humidity required for sclerotial germination. For SR + AgNPs treatment, after placing sclerotia on the collar region, AgNPs suspension was sprayed with automizer over this and then covered with absorbant cotton soaked in AgNPs suspension. The infection in collar region by S. rolfsii was observed after 24 h of inoculation.
Chromatographic detection and quantification of phenolic compounds in chickpea. Extraction of phenolic compounds was done following the protocol described by Niranjan et al. 43 . For extraction purpose, 1.0 g of plant sample collected (after 24 h of pathogen challenge) in triplicate from each treatment is further processed separately in order to obtain the data in triplicate. Plant sample was crushed with 10 ml of methanol:water:hydrochloric acid solution (5:4:1, v/v) in a mortar and pestle and left overnight in orbital shaker at room temperature. After this, the mixture was filtered through Whatman No. 1 filter paper and plant residue was further extracted twice with same solution for maximum extraction of phenolic compounds. The filtered plant extract was combined together and concentrated upto half of the volume using rotary evaporator (Eyela N-N series, Tokyo, Japan). The residue was further fractionated three times with Ethyl acetate. The collected ethyl acetate fraction was concentrated under reduced pressure on rotary evaporator. The obtained residue was dissolved in 1.0 ml of HPLC grade methanol and filtered through a 0.2 μ m membrane filter (Merck). This stock solution was subjected to HPLC for detection and quantification of phenolic compounds.
For HPLC analysis, 20 μ l of sample was injected into C-18 HPLC (4 μ m, 250 × 4.6 mm, Phenomenex, USA) using HPLC system (Shimadzu, Japan) equipped with LC-10 dual pump and UV detector SPD-10A. The mobile phase used for compounds separation was a linear gradient prepared from acetic acid (1% v/v) in HPLC grade water (pump A) and acetonitrile (pump B), with detection at 254 nm. The flow rate was maintained at 1.0 ml/min. Results were obtained by comparisons with standards using data integrated by Shimadzu class VP series software. Phenolic compounds were detected in sample by comparing retention time (RT) of peaks with that of standard and further quantified by comparing peak area in the sample with that of standard. H 2 O 2 detection in leaves by DAB (3,3′-diaminobenzidine) staining method. Subcellular localization of H 2 O 2 in chickpea leaves was done using the protocol described by Thordal-Christensen et al. 44 . Leaf sample was collected from 6 independent plants of each treatment. DAB staining solution is prepared by dissolving 50 mg of DAB in 45 ml of sterile distilled water and final pH was set to 3 using 0.2 M HCl. After this 0.05% of Tween 20 together with 2.5 ml of 200 mM Na 2 HPO 4 was added to DAB solution. DAB solution is stored in dark brown bottle as it is light sensitive. For staining purpose, leaf sample was dipped overnight in DAB solution in dark condition at room temperature. After this, leaves were removed from DAB solution and further boiled in bleaching solution containing alcohol and acetic acid (3:1) till leaves become clear (completely devoid of chlorophyll). The boiling step will bleach out the chlorophyll so that brown precipitate formed by reaction of DAB with H 2 O 2 remains in the leaves. For detection of brown precipitate, leaves were visualized under light microscope (Nikon DS-fi1, Japan).
Histochemical staining for stem lignification. After 24 h of pathogen challenge, plants were harvested and chickpea stem was used for microscopic investigation of lignification pattern in each treatment using the protocol as described earlier 24,45 . Transverse sections of stem were stained in saturated aqueous solution of phloroglucinol in 20% HCl and immediately observed under light microscope for lignification as indicated by red-violet color.

Results and Discussion
Identification of BHU-S7. The bacterial strain BHU-S7, isolated from agricultural farm soil was identified as Stenotrophomonas sp. using 16S rDNA sequencing analysis. The nucleotide sequence of 1445 bp was phylogenetically characterized using BLAST tool of NCBI search. The constructed phylogenetic tree indicated that the bacterial strain BHU-S7 shared a maximum 99% close homology with Stenotrophomonas sp. (Fig. 1).
Nucleotide sequence accession number and MTCC number. The partial nucleotide sequences for 16S rDNA of the bacterial strain BHU S-7 has been submitted to Genbank under the accession number KF863907. Furthermore, pure culture of the bacterial strain has also been deposited at IMTECH, Chandigarh, India with MTCC number 5978.
BHU-S7 isolated from agricultural soil was used for biosynthesis of AgNPs. The visible appearance of dark brown color in culture supernatant upon addition of AgNO 3 confirms successful extracellular synthesis of AgNPs. In the whole biosynthesis process, the noticeable color change of culture supernatant from yellow to dark brown is due to reduction of silver ions Ag + into Ag° by using active biomolecules present in culture supernatant 46,47 . However, no color change was observed in control set where plain growth media was treated with 1 mM AgNO 3 indicating the functional involvement of bacterial biomolecules in reduction process leading to biosynthesis of AgNPs. The development of brown color in the reaction mixture is mainly attributed to excitation of surface plasmon resonance, a unique optical property of noble metals 48,49 . Interestingly, the most widely accepted mechanism for extracellular biosynthesis of AgNPs is via extracellular enzymes such as nitrate reductase enzyme present in supernatant that help in transferring the electron to silver ion and hence reduced to AgNPs 47,50 . Characterization of biosynthesized AgNPs. Optical. The unique surface plasmon resonance (SPR) property of noble metals strongly induces the absorption of the incident light and thus can be monitored by Uv-Visible spectroscopy 51,52 . Moreover, this SPR band is more prominent for noble metal nanoparticles particularly for AgNPs and AuNPs 53 . Hence, in the present study, the biosynthesis of AgNPs was ascertained by Uv-visible spectroscopy that displayed a strong surface plasmon resonance (SPR) peak at 440 nm ( Fig. 2). It is evident from previous reports that AgNPs exhibit UV-visible absorption spectra in the range of 400-500 nm due to Mie scattering 51 . Therefore, presence of characteristic sharp and clear peak at 440 nm indicates successful biosynthesis of AgNPs. While on other side, this distinctive peak was absent in control set signifying no reduction of Ag ions. The reduction process of silver ions and the biosynthesis of stable AgNPs occurred within 24 hour of reaction.
Structural. The crystallinity of biosynthesized AgNPs was confirmed by X-ray diffraction (XRD) analysis that determines size, lattice and structure of nanoparticles 54 . The diffractogram showed well resolved four diffraction peaks at 2θ angles of 38.39°, 49.25°, 64.10°, and 77.87° which were indexed to the Bragg reflection peaks of (111), (200), (220), and (311) planes of face centered cubic (fcc) structures of AgNPs, respectively (Fig. 3a). In this experiment, the XRD data confirmed that the synthesized nanoparticles were crystalline in nature and had a face-centered cubic structure. Further, the average crystallite size (d) of biosynthesized AgNPs was calculated following the Debye-Scherrer formula: where k = 0.9 is the shape factor, λ is the X-ray wavelength of Cu Kα radiation (1.54 Å), θ is the Bragg diffraction angle, and B is the full width at half maximum of the (111) plane diffraction peak 55 . The calculated average crystallite size was estimated to be 12.7 nm.
Morphological. The morphological investigation of the biosynthesized AgNPs was carried out using SEM and TEM analysis. The Fig. 3b shows the SEM micrograph recorded from dry mass of biosynthesized AgNPs, which was deposited on a carbon tape. The micrograph clearly demonstrated the aggregation of micro particles under the powder form. However, the narrow distribution of AgNPs in the TEM analysis was in accordance with the UV-visible spectral study. The presence of single SPR peak as revealed by UV-visible spectroscopy divulges spherical shape of AgNPs 56 . In the present study, TEM analysis confirms the existence of spherical AgNPs with slight agglomerations at some places that may be due to presence of biological macromolecules on their surfaces (Fig. 3c). Moreover, AgNPs represented variable size ranging from 5 to 30 nm with average mean size estimated to be ~12 nm. However, such variations in size are probably due to the fact that AgNPs were being synthesized at different times 57 .
Elemental. The compositional analysis of the biosynthesized AgNPs was carried out by Energy dispersive X-ray (EDAX). The EDAX spectra displayed characteristic signal peak of silver element (Ag) that confirmed the crystallinity and mettalic nature of biosynthesized AgNPs (Fig. 4a). It is worth mentioning here that silver nanocrystallites exhibit distinctive absorption peak at 3 keV because of surface plasmon resonance 58 . Therefore, this data reveal successful synthesis of AgNPs as maximum proportion of total elemental composition is covered by silver followed by carbon (C) and oxygen (O). The occurrences of carbon and oxygen peaks may be due to the biological macromolecules like proteins and enzymes present on the surface of AgNPs.
Functional. FTIR analysis was performed in order to gain functional knowledge about the biological macromolecules (that possibly act as reducing/stabilizing agent) present in the culture supernatant of Stenotrophomonas sp. BHU-S7. The FTIR spectrum recorded from the dried powder of AgNPs is shown in Fig. 4b. The peaks near 3421 cm −1 and 2901 cm −1 were assigned to N-H stretching and C-H stretching, respectively. The peak at 1627 cm −1 corresponds to amide I, arising due to carbonyl stretch in enzymes and proteins. The broad peak at Thermal. Thermal stability of the biosynthesized AgNPs was examined by TGA where temperature aided decomposition/desorption behavior of the particles is studied 59 . It has been observed from TGA plot that total dominant weight loss of 37.87% occurred in two steps in the temperature range of 0 °C to 700 °C while 62.13% of  residual weight remained in the sample (Fig. 4c). The first step weight loss corresponding to 9.91% was observed at ~100 to 200 °C and the second step weight loss (27.96%) appeared in the temperature range of ~300-450 °C. The first step weight loss can be attributed to evaporation of water molecules adsorbed on the surface of AgNPs whereas second step weight loss is due to desorption of bioorganic components such as proteins and enzymes present in AgNPs sample.

Proficiency of biosynthesized AgNPs by
Stenotrophomonas sp. BHU-S7 as nanofungicide against phytopathogens. AgNPs being the most effective and popular antimicrobial agent have capacity to kill nearly 650 types of pathogenic microbes including bacteria, fungi, viruses etc. within 30 minute 60 . The broad spectrum antimicrobial potency of AgNPs is a well-documented fact and has been widely described in many reports [61][62][63][64][65] . Similarly, several lines of evidence also describe potential antagonistic activity of AgNPs against diverse range of phytopathogenic fungi [66][67][68][69] . The idea of using biosynthesized AgNPs using biological agents for efficient management of plant diseases has gained noteworthy attention due to the fact that this biosynthesis process involves non-toxic and low cost biomolecules 26 . Moreover, biosynthesized AgNPs being equally competent to those nanoparticles generated by physical and chemicals methods provide safe and environment friendly approach for plant disease management. In context to this, several reports have successfully assessed the strong antifungal activity of biosynthesized AgNPs against phytopathogens 24-26,31,32,70 .
As pointed above, the present investigation emphasizes the sturdy impact of AgNPs biosynthesized using agricultural isolate of Stenotrophomonas sp. on some devastating plant pathogens such as A. alternata, C. lunata, B. sorokiniana and S. rolfsii. We examined the probable impact of biosynthesized AgNPs on conidial germination of foliar phytopathogens A. alternata, C. lunata and B. sorokiniana as this is the main disease causing step. Our data lucidly depict significant complete inhibition in conidial germination at 2, 4 and 10 μ g/ml concentration under in vitro condition. While, on the contrary 100% conidial germination was observed in control set. In AgNO 3 control set 20-30% inhibition was reported indicating superiority of AgNPs over AgNO 3 in controlling plant diseases (Fig. 5a,b,c). The successful conidial germination over leaf surfaces is the main disease determining step leading to development of serious foliar diseases 71 . Hence, AgNPs mediated inhibition in conidial germination of such phytopathogens at very low concentration is of great importance and can be successfully applied for controlling devastating foliar diseases such as leaf spot, sheath blight, spot blotch etc. 24,70 . Additionally, we also examined the biocontrol potential of biosynthesized AgNPs against S. rolfsii, a soil-borne plant pathogen causing serious diseases on a variety of horticultural and agricultural crops. The efficient management of this soil borne plant pathogen is challenging and difficult as well because of its long term survival in soil due to presence of sclerotia 72 . Moreover, these hard structured sclerotia are well adapted for survival under stressed environment and resistant to physical and chemical degradation due to melanin accumulation in the outer membrane 73 . Therefore, we were more interested in studying the inhibitory impact of biosynthesized AgNPs on sclerotia germination. Our result clearly indicated that AgNPs treatment for 24 h completely reduced the sclerotia germination in PDA medium (Fig. 5d) while there was partial inhibition of sclerotia germination after 12 h treatment with AgNPs (data not shown). Exciting results were also obtained in soil system where noticeable reduction in sclerotia germination occurred after AgNPs treatment while in control set sclerotia started germinating after 24 h of incubation (Fig. 5e). AgNPs generate highly reactive Ag + ions which is actually responsible for its antimicrobial activity. Indeed, processes such as penetration into microbial cell, disruption of transport system, accumulation of Ag + ions, and production of reactive oxygen species are the definite modes of actions of AgNPs responsible for its cidal effect on microbes 74,75 . Hence, it can be hypothesized that inhibitory effect of biosynthesized AgNPs on these phytopathogens is mainly attributed to one of these mechanisms. However, for verifying the exact mechanism a detail study is required.
Biosynthesized AgNPs mediated suppression of collar rot of chickpea. S. rolfsii causes collar rot disease in chickpea leading towards 50-95% mortality at seedling stage. The disease is more prevalent in attacking chickpea seedlings (maximum upto 4-6 weeks after sowing) under favorable condition i.e. high soil moisture and warmer climate 76 . The distinctive disease symptom is characterized by rotting of collar region due to development of whitish mycelial coating followed by yellowing and further collapsing of young seedlings. In the present investigation, greenhouse experiment revealed that AgNPs treatment resulted into suppression of collar rot of chickpea. No characteristic disease symptoms developed at the site of infection i.e. collar region after 24 h of pathogen challenge. Interestingly, chickpea plants looked as green and healthy as in control (without pathogen challenge) set. While in contrary, 100% mortality was observed in pathogen challenged set where plants got collapsed as a result of rotting at collar region after 48 h of pathogen inoculation (Fig. 6). These findings clearly indicated that AgNPs treatment provided protection to chickpea plants against Sclerotium rolfsii by hindering sclerotia germination. Our results represent direct evidence of interaction between sclerotia and biosynthesized AgNPs suggesting that reduced sclerotia germination is actually responsible for diminished inoculum potential and disease evidence. Furthermore, it can be hypothesized that such effects of AgNPs might be associated with disruption of sclerotial rind due to Ag + penetration followed by their toxic accumulation inside the cell.

Defense response induced by phenolics in AgNPs treated chickpea against S. rolfsii infection.
Phenolic compounds are known to confer disease resistance in plants against pathogen attack. Several mechanisms are involved in phenolic compounds mediated plant defense response that primarily includes building physical/chemical barrier through production of phytoanticipins (preformed) and phytoalexins (induced) and triggering signaling molecules for defense gene induction either locally or systemically [77][78][79][80][81] . It is well documented that diverse array of phenolic acids and flavonoids (phenolic acids derivatives) are synthesized in plants through phenylpropanoid pathway, by products of monolignol pathway and breakdown products of lignin 78,82 . Redeeming the immense importance of phenolics in plant-microbe interactions, we attempted to corroborate qualitative and quantitative differences in phenolics in response to S. rolfsii infection and biosynthesized AgNPs treatment.
The phenolic profiles revealed quantitative variations in phenolic compounds among the three treatments (Fig. 7a). The result indicated that most of the phenolic compounds were maximally induced in S. rolfsii challenged chickpea plants followed by maximal induction of ferulic acid and myricetin in AgNPs treated challenged (SR + AgNPs) plants. In general, the pattern of phenolic acids induction was observed to be as SR control > SR + AgNPs> Control ( Table 1). The maximally induced phenolics in SR challenged plants were found to be shikimic acid (1170 μ g/g), gallic acid (53.3 μ g/g), syringic acid (118.4 μ g/g), p-coumaric acid (232 μ g/g), salicylic acid (547 μ g/g), abscisic acid (11.7 μ g/g), querecetin (46.2 μ g/g), kaempferol (324 μ g/g). Interestingly, many fold  increase in kaempferol (324 μ g/g) was reported in pathogen challenged plants as compared to control (10.05 μ g/g) and SR + AgNPs (53.5 μ g/g) plants. Apart from this, pathogen challenged chickpea plants treated with AgNPs experienced induction of ferulic acid (206 μ g/g) and myricetin (121 μ g/g) as compared to control and SR control plants. This marked differences in phenolics content among the treatments demonstrated that upon exposure to S. rolfsii, the chickpea plants felt stress and exhibited maximum induction of phenolic compounds resulted due to plant's inherent immunity response in order to fight against the biotic stress. The maximally induced phenolic acids are known to exhibit antioxidant and antimicrobial property 83,84 . Alternatively, the direct contact between AgNPs and sclerotia weakened further progression and invasion of pathogen inside the host plant in SR + AgNPs treatment. Consequently, plants sensed relatively lesser stress and hence we observed not much difference in phenolic compounds between control and SR + AgNPs treatment. However, when compared with SR challenged plants, the increased induction of ferulic acid and myricetin was observed in SR + AgNPs treatment. Antioxidant property of ferulic acid and myricetin has been well documented in earlier reports [85][86][87][88] . Furthermore, ferulic acid is known to provide cell wall rigidity by building crosslink between polysaccharides and lignin [89][90][91] . These reports strongly indicate the potential role played by ferulic acid and myricetin against pathogen attack by making physical barrier and scavenging effect in response to free radicals generated upon exposure to S. rolfsii.

AgNPs mediated impact on lignification and H 2 O 2 production in chickpea and their role in plant defense.
Lignin is an important cell wall component in vascular plants that structurally strengthen and provide rigidity to the cell wall via cross linking with polysaccharides 92,93 . Lignification of plant tissue has been evidenced as an important mechanism of plant defense against pathogen attack by building a physical barrier to inhibit pathogen invasion inside the host plant cell 94 . Therefore, in the present investigation we attempted to examine the impact of AgNPs treatment on lignification pattern following pathogen attack. Interestingly, maximum lignification was observed in S. rolfsii challenged (SR control) chickpea plants followed by moderate lignification in SR + AgNPs treatment and least in control unchallenged plants. This differential response among the treatments resulted due to activation of plant's inherent immunity response towards pathogen challenge and AgNPs treatment. Our findings point to positive correlation between increased lignification and severe stress condition 95 . Enhanced lignin deposition in cell wall in order to reduce the growth or confine the invading pathogen has been well described in earlier reports [96][97][98] . Despite of this very well-known fact, the direct impact of AgNPs on plant lignification pattern is a largely unexplored aspect. In relation to this, our study explores the probable impact of AgNPs on plant defense response towards pathogen attack. We evidenced that direct interaction between AgNPs and S. rolfsii gave rise to relatively reduced lignin deposition attributed to diminished pathogenicity as compared to SR control. Undoubtedly, it appears that AgNPs potentially exerted its toxic effect on S. rolfsii and hence SR + AgNPs treated plants experienced relatively lesser stress and displayed modification in defense response. The almost similar trend of lignification pattern in control and SR + AgNPs treatment revealed immense role of AgNPs in providing protection to chickpea plants against pathogen attack (Fig. 7b). Apart from this, the strong evidence for AgNPs mediated protection to chickpea plants against S. rolfsii infection is well determined by studying in situ accumulation of H 2 O 2 in plants using DAB staining method. In the present study, maximum number of brown spots indicative of H 2 O 2 production appeared in pathogen challenged (SR control) chickpea leaves. Remarkably, the area and intensity of brown spots were highest due to S. rolfsii infection. In contrast to this, unchallenged control plants and SR + AgNPs treated plants displayed similar trend of brown coloration in leaves. It is important to note that the intensity of brown staining was relatively very low in these two treatments as compared to SR control (Fig. 7c). It is evident from earlier reports that H 2 O 2 being the most stable reactive oxygen species (ROS) is thought to regulate plant development as well as stress response 99,100 . Moreover, H 2 O 2 production in plants is indicative of an early response towards pathogen attack 101 . The results presented here strongly suggest that H 2 O 2 production increased tremendously following S. rolfsii attack in SR control treatment. This elevated level is attributed to early response of chickpea plants to stress condition imposed by S. rolfsii by triggering its innate defense response. Plants accumulate higher level of ROS under stressed environment however, at low level they act as signal for triggering other defense response whereas their excessive accumulation lead to oxidative damage to protein, lipid and DNA resulting into plant death 102,103 . In relation to this, it can be hypothesized that collapsing of chickpea plants following S. rolfsii infection could be due to adverse impact of excessive H 2 O 2 production on plant growth and other metabolic activity including lipid peroxidation, oxidative damage etc. On other hand, comparatively reduced level of H 2 O 2 production in SR + AgNPs treated plants provides convincing evidence of important role played by AgNPs in providing protection to chickpea plants against S. rolfsii. It indicated that AgNPs treated plants are well equipped to counteract with pathogen challenge by increasing the activity of antioxidant enzymes that reduced the level of ROS and further improved stress tolerance.

Conclusion
The data presented in this article opens new perspective for efficient agricultural implications of bacterial strain Stenotrophomonas sp. that has not been attempted before. This study concerns the broad range antifungal properties of AgNPs biosynthesized using agricultural isolate of Stenotrophomonas sp. BHU S-7 (MTCC 5978), against devastating foliar and soil-borne phytopathogens. The biosynthesized AgNPs have been shown to adversely affect pathogenic propagules such as conidia and sclerotia leading to their reduced germination that ultimately diminished the future possibility of disease incidence. Additionally, the biosynthesized AgNPs exhibited successful management of chickpea collar rot disease caused by S. rolfsii under greenhouse condition. It is important to note that apart from in vitro studies, we made attempt to decipher the proficiency of biosynthesized AgNPs in natural environment for successful practical implication of this work in near future. The biosynthesized AgNPs mediated efficient management of collar rot disease was believed to be operated by many mechanisms. The reduced sclerotia germination, induction of phenolic acids, altered lignification and H 2 O 2 production was the most reasonable Scientific RepoRts | 7:45154 | DOI: 10.1038/srep45154 explanation of the protective impact of AgNPs on chickpea against S. rolfsii infection (Fig. 8). The almost similar trend of phenolic profiling, stem lignin deposition and H 2 O 2 production in unchallenged control and SR + AgNPs treatments revealed that AgNPs treated plants experienced lesser stress and are better equipped to cope with pathogen challenge. It also explains that AgNPs treatment helped in reducing the oxidative stress by enhancing the activity of antioxidants enzymes as evident by lowered level of H 2 O 2 production in comparison to its excessive content in pathogen challenged plants. However, further investigations on studying the level of different antioxidant enzymes are required to support the proposed detail of mechanism. Altogether, the evidence achieved in the present study strengthen the perspective of robust and conceivable applications of AgNPs biosynthesized using greener approach and environment friendly Stenotrophomonas sp. BHU-S7 in agricultural sector. Moreover, we have gained new insight about the future possibilities of agricultural isolate of Stenotrophomonas sp. particularly for environmental benefits. Rethinking the debate addressing distinction between beneficial and harmful Stenotrophomonas strains, we strongly emphasize the selection of agricultural isolates of Stenotrophomonas sp. which enable their successful applications in agriculture. This may also be explained by the fact that pathogenic and non-pathogenic Stenotrophomonas strains share completely different niches and are likely to be adapted to that environment.