The endophyte Stenotrophomonas maltophilia EPS modulates endogenous antioxidant defense in safflower (Carthamus tinctorius L.) under cadmium stress

The endophyte Stenotrophomonas maltophilia EPS modulates endogenous antioxidant defense in safflower (Carthamus tinctorius L.) under cadmium stress | Research Square window.SnipcartSettings = { analytics: { enabled: false } }; (function() { var accessVector = localStorage.getItem('access_vector') || ''; window.dataLayer = window.dataLayer || []; if (accessVector) { window.dataLayer.push({ user: { profile: { profileInfo: { snid: accessVector } } } }); } })(); (function(w,d,s,l,i){w[l]=w[l]||[];w[l].push({'gtm.start':new Date().getTime(),event:'gtm.js'});var f=d.getElementsByTagName(s)[0],j=d.createElement(s),dl=l!='dataLayer'?'&l='+l:'';j.async=true;j.src='https://www.googletagmanager.com/gtm.js?id='+i+dl;f.parentNode.insertBefore(j,f);})(window,document,'script','dataLayer','GTM-K279D39R'); Browse Preprints In Review Journals COVID-19 Preprints AJE Video Bytes Research Tools Research Promotion AJE Professional Editing AJE Rubriq About Preprint Platform In Review Editorial Policies Our Team Advisory Board Help Center Sign In Submit a Preprint Cite Share Download PDF Research Article The endophyte Stenotrophomonas maltophilia EPS modulates endogenous antioxidant defense in safflower (Carthamus tinctorius L.) under cadmium stress Noura Sh. A. Hagaggi, Usama M. Abdul-Raouf This is a preprint; it has not been peer reviewed by a journal. https://doi.org/ 10.21203/rs.3.rs-1538673/v1 This work is licensed under a CC BY 4.0 License Status: Under Review Version 1 posted 8 You are reading this latest preprint version Abstract Cadmium (Cd) pollution in agricultural soils induces oxidative stress in plants that in turn is the foremost limiting factor for agricultural productivity. In past few decades, metal binding ability of microbes is of great interest as an emerging environmentally friendly technology that can be exploited to alleviate metal stress in plants. Considering these, in the present study an endophytic bacterium strain EPS has been isolated from the roots of common bean. The 16S rRNA sequence revealed its identity closely similar to Stenotrophomonas maltophilia . The strain showed tolerance to Cd stress up to 200 mg L − 1 Cd 2+ . The inoculation of strain EPS in safflower seeds significantly enhanced the antioxidant defense of plants under Cd-stress conditions throught increasing the levels of antioxidant molecules like phenolics, flavonoids and carotenoids as well as improving the activities of the antioxidative enzymes including guaiacol peroxidase (POX), ascorbate peroxidase (APX) and superoxide dismutase (SOD). The output of this study is that strain EPS inoculation mitigates Cd-induced oxidative damage and consequently strain EPS may be beneficial, especially in Cd-contaminated crop fields. Cadmium Antioxidant Safflower Stenotrophomonas maltophilia Figures Figure 1 Figure 2 Figure 3 Figure 4 Introduction Over wide world, heavy metals accumulation in agricultural soils is a serious problem threats crop production (He et al. 2015 ; Rizwan et al. 2016a ). Heavy metals are among the most main causes of environmental stresses. Overaccumulation of heavy metals in the soils causes dangerous phytotoxicity that can store in plants and easy transmit through the food chain resulting in negatively impact on human and animal health (Fryzova et al. 2017 ). Hyperlevels of heavy metals alter normal plant functions and metabolism causing repression of vital processes such as photosynthesis, respiration, and enzymatic activities (Hossain et al. 2012 ). On the other hand, high levels of heavy metals can induce excess generation of reactive oxygen species (ROS) as well as cytotoxic compounds, leading to oxidative stress via demolishing the equilibrium between prooxidants and antioxidants within the plant cells (Zengin and Munzuroglu 2005 ; Hossain et al. 2012 ; Sytar et al. 2013 ). This results in cellular damage as well as decreasing plant productivity (Raja et al. 2017 ). Cadmium (Cd) is non-essential element for living organisms, and it is highly toxic to plants and animals even at very low concentrations (Dai et al. 2012 ). Cadmium mainly originates from industrial processes and phosphate fertilizers, releases into agricultural lands and has long biological half-life (Gill et al. 2013 ). In plants, the exposure to cadmium induces numerous hazards physiological and growth changes as well as oxidative stress by generating ROS, that react with lipids, proteins, pigments and nucleic acids in the plant cell, leading to cellular damage and consequently decreasing productivity (Romero-Puertas et al. 2004 ). Furthermore, cadmium also can transfer into human via food chain and can result in kidney, bone and lung diseases (Bernard 2008 ). Traditional remediation techniques for heavy metal-contaminated soils are expensive and destructive to environment (Meagher 2000 ). Therefore, scientists and engineers intensify their efforts to find cost effective and safe technologies (Boyajian and Carreira 1997 ; Wasay et al. 1998 ). Most of plant associated microorganisms are metal resistant, whose application in heavy metal contaminated soils can improve metal immobilization in soils and plant biomass (Ma et al. 2011 ; Ma et al. 2016 ). Despite that the applications of some potential bacterial strains to remediate soils contaminated with heavy metals have been reported, it is urgent to search a new microbial resources that can be used efficiently in heavy metals remediation (Tirry et al. 2018 ). Safflower ( Carthamus tinctorius L.) is herbaceous annual plant belongs to family Asteraceae. It is cultivated from prehistoric times throughout many areas with temperate climates over the world including southern Asia, China, India, Iran and Egypt (Dordas and Sioulas 2008 ; Weiss 2000 ). Safflower is commercially used for vegetable oil extraction, as well as in the traditional medicine for the treatment of rheumatism, paralysis, vitiligo, psoriasis and mouth ulcers (Delshad et al. 2018 ). Moreover, it has numerous pharmacological activities i.e, antioxidant, analgesic, anti-inflammatory and antidiabetic activities (Asgarpanah and Kazemivash 2013 ). It has been reported that safflower plants can accumulate high levels of Cd in their roots and leaves (Shi et al. 2010 ; Namdjoyan et al. 2011 ). Although, some scientific data exists on the antioxidant defense mechanisms in response to cadmium stress in safflower cultivars (Namdjoyan et al. 2011 ), to our knowledge, there is no study dealing with alleviation of Cd- induced oxidative stress in safflower by using bacteria. Therefore, the present work was designed to investigate the potentiality of the endophytic bacterium Stenotrophomonas maltophilia strain EPS to alleviate Cd-induced oxidative stress in safflower plants. Materials And Methods Isolation and identification of endophytic bacteria Healthy fresh roots of common bean plants ( Vigna unguiculata L.) were collected in sterile plastic bags from Aswan University greenhouse. Immediately nodules were surface- sterilized using 70 % ethanol (30 sec) followed by 5 % sodium hypochlorite (3 min) and then washed three times with sterilized distilled water (Vincent 1970). Under aseptic conditions, nodules were crushed in a test tube contained one mL of sterilized saline solution. Loopful of the obtained suspension was streaked on the surface of tryptic soy agar and nutrient agar plates. Plates were incubated at 37 o C for 72 h for the appearance of colonies. The ribosomal (16S rRNA) gene of the selected strain was amplified using 27F and 1492R primers (Frank et al. 2008) in Applied Biotechnology lab at Ismailia, Egypt. PCR product was sent to SolGent Co., Ltd., South Korea for sequencing. Then, the similarity of the obtained sequence was evaluated based on BLAST outputs using NCBI reference sequence database. Neighbor-joining phylogenetic tree of the strain was constructed using MEGA X 10.1.7 software (Kumar et al. 2018). Cd tolerance of the strain Maximum tolerable concentration (MTC) of cadmium by the strain was determined according to the method of Vashishth and Khanna (2015), with slight modification. Briefly, 10 mL of yeast extract-mannitol broth (YMB) in glass tubes was supplemented with different concentrations of CdCl 2 i.e., 0 (control), 50, 100, 150, 200, 250 and 300 mg L -1 . 10 mL of YMB without CdCl 2 was used as control. Tubes were inoculated with 1 mL of inoculum (10 7 CFUmL -1 ), and incubated for 48 h at 28 o C and 150 rpm. The optical density (OD) was measured at 600 nm. The highest concentration of cadmium (CdCl 2 ) that allowed visible bacterial growth after 48 h of incubation was considered as the maximum tolerable concentration (MTC). Evaluation of Cd- adsorption potential of the strain The ability of the whole culture of the present strain (cells and supernatant) for adsorping cadmium was evaluated using the method of Du et al. (2016 b). 100 mL of the whole culture broth contained 50 and 100 mg L -1 of CdCl 2 was shaken at 120 rpm and 28 o C for 24 h. Cells were then removed by centrifugation. Concentration of the residual, non-adsorbed metal ion in the solution was estimated by atomic absorption spectrophotometer (Thermo Scientific™ iCE™ 3000). Experiment was performed in triplicate. The adsorption efficiency (%) was calculated according to the following formula: where Cdi and Cde are the concentration of initial and equilibrium Cd ion in the solution (mgL -1 ) respectively. Seed inoculation and pot experiment Seeds of safflower (cv. Giza-1) were obtained from Faculty of Agriculture and Natural Resources, Aswan University. Seeds were surface sterilized with 70 % ethanol for 3 min, rinsed three times with sterilized distilled water. Seeds thereafter were soaked in a freshly prepared bacterial suspension (1×10 8 CFU mL -1 ) for 1 h, and left to dry before sowing. Seeds used for control were soaked in sterilized distilled water. Seeds were sown in pots containing an autoclaved mixture of clay and sand (1:1 w/w), with maintaining field capacity at 90 %. Pots were kept under normal climatic conditions. After three weeks of sowing, five homogenous plants in each pot were subjected to three Cd treatments including 0 (control), 50 and 100 mg L -1 of CdCl 2 . After three weeks of cadmium exposure, healthy expanded leaf samples were collected, frozen and then used for measuring the defensive non-enzymatic and enzymatic antioxidant activities. The experiment was repeated twice. Estimation of hydrogen peroxide (H 2 O 2 ) content To evaluate the H 2 O 2 content of the leaves, the method of Velikova et al. (2000) was followed. One gram of fresh leaves was homogenated in 10 mL trichloroacetic acid (0.1 %) using a mortar and pestle, and then centrifuged. To 0.5 mL of the supernatant, 0.5 mL of potassium phosphate buffer (pH 7.0) and 1 mL of 1 M KI were added. The mixture was vortexed, and the absorbance was read at 390 nm. A calibration curve of different concentrations (µmol) of 30 % (v/v) H 2 O 2 was used as standard. Assessments of non-enzymatic antioxidants Total phenolics The Folin-Ciocalteu assay described by Singleton et al. (1999) was followed to determine the total phenolic compounds in the leaves extracts. Absorbance was read at 700 nm, and the content of total phenolics was expressed as mg gallic acid equivalents per gram of fresh weight using gallic acid as a reference. Total flavonoids Aluminum chloride method according to Chang et al. (2002) was used for quantifying the total contents of flavonoids of the extracts. The absorbance was recorded at wavelength 510 nm. The concentration of flavonoids was calculated from quercetin calibration curve as mg quercetin equivalents per gram of fresh weight. Total carotenoids Pigments were extracted from fresh leaves and their contents were estimated as described by Lichtenthaler and Wellburn (1983). One gram of fresh leaves was macerated in 80 % acetone, the supernatant was filtered and makeup to 50 mL with the solvent. The total contents of chlorophylls a (Chl a), chlorophylls b (Chl b) and carotenoids were measured by reading the absorbance at wavelengths 646, 663 and 440.5 nm respectively. The content of each pigment was calculated in mg per gram of fresh weight using the following equations: Chl a (mg g f.wt. - 1 ) = (12.21×A 663 ) - (2.81×A 646 ) Chl b (mg g f.wt. - 1 ) = (20.13×A 646 ) – (5.03×A 663 ) Carotenoids (mg g f.wt. - 1 ) = (4.69×A 440.5 ) - 0.268× (Chla + Chlb) Total antioxidant capacity Total antioxidant capacity of the ethanolic extracts of the leaves was measured per gram of fresh weight as mg ascorbic acid equivalents using ascorbic acid standard curve, according to phosphomolybdnum assay (Prieto et al. 1999). Assessments of enzymatic antioxidants Antioxidant enzymes were extracted from fresh leaves according to Cavalcanti et al. (2004) with slight modification. One gram of fresh leaves was homogenized using a mortar in 10 mL of extraction buffer containing 0.2 M of potassium phosphate buffer (pH 7.2), 0.1 mM EDTA and 1 mM phenylmethylsulfonyl fluoride as proteinase inhibitor. The homogenate was filtered. The obtained filtrate was used for enzymatic assays. Catalase (CAT) activity Catalase activity was estimated by the method of Kato and Shimizu (1987). To 3 mL of the reaction mixture containing 50 mM potassium phosphate buffer (pH 7.0) and 20 mM H 2 O 2 , 100 µl of enzymatic extract was added. The decrease in H 2 O 2 was followed as decline in optical density at 240 nm. Catalase activity was calculated with the extinction coefficient of H 2 O 2 (40 mM −1 cm −1 ), and expressed as 1μmol of H 2 O 2 decomposed per minute under assay conditions. Guaiacol peroxidase (POX) activity The activity of guaiacol peroxidase enzyme was determined following the method of Kim and Yoo (1996). Briefly, the reaction mixture contained 0.2 mL of enzyme extract, 0.8 mL of phosphate buffer (0.2 M, pH 7.2), 1 mL of guaiacol (15 mM) and 1 mL of hydrogen peroxide (3 mM) was incubated for 10 min at 30 °C. Reaction was terminated using 0.5 mL of H 2 SO 4 (5 %), and the absorbance was read at 470 nm. POX activity was calculated using the extinction coefficient of oxidation product (tetraguaiacol), (ε470= 26.6 mM cm -1 ) as follow: U/mL = [Change in absorbance min −1 × Reaction mixture volume (mL) × Dilution factor]/ [ε470× Enzyme extract volume (mL)] Ascorbate peroxidase (APX) activity Ascorbate peroxidase activity was evaluated according to Senthilkumar et al. (2021). To 0.8 mL of a reaction mixture contained potassium phosphate buffer (50 mM), ascorbic acid (0.5 mM), H 2 O 2 (1.0 mM) and EDTA (0.1 mM), 0.2 mL of the enzyme extract was added. After 30 s the decrease in absorbance at 290 nm was followed up to 60 s with an interval of 15 s. One unit of enzyme activity was expressed as the amount of enzyme required to oxidize 1 μmoL of ascorbic acid per minute with absorbance coefficient 2.8 mM cm at 290 nm. Superoxide dismutase ( SOD ) activity Superoxide dismutase activity was estimated according to Van Rossun et al. (1997). Three mL of reaction mixture contained 50 mM sodium phosphate buffer (pH 7.6), 0.1 mM EDTA, 50 mM sodium carbonate, 50 μM nitroblue tetrazolium (NBT), 10 μM riboflavin, 12 mM L-methionine and 100 μl of crude extract. Tubes contained the same reaction mixture without enzyme extract used as control. The tubes were placed under two 15 W fluorescent lamps for 15 min to start the reaction. The absorbance was recorded at 560 nm. One unit of SOD activity was defined as the amount of enzyme which reduced the absorbance to 50 % compared with the control. Statistical analysis Experimental data were compared using one-way analysis of variance (ANOVA) with Tukey's HSD test. Values were expressed as means ± standard errors (SEs) of three biological replicates from two independent experiments. Differences were considered significant if p ≤ 0.05. Results And Discussion Metal toxicity and stress in plants triggering the excessive accumulation of ROS in mitochondria, chloroplast, and peroxisomes (Kochian et al. 2004), resulting in imbalance between the generation of ROS and antioxidant defense systems, that in turn causes oxidative stress to plants (Gupta et al. 2013). Oxidative stress disturbs physiological and metabolic processes of the plants leading to a limitation in plant growth, crop production and yield, and consequently causes massive agricultural loss (Tran and Popova 2013). Recently, plant root-associated bacteria are globally used for the amelioration of crop performance to encounter heavy metal contamination in agricultural soils (Mitra et al. 2018b; He et al. 2020; Ghosh et al. 2022). Identification of isolated strain The selected strain was coded as EPS. The NCBI- BLAST analysis of strain EPS sequence showed closely similarity with percent identity of 100 % to Stenotrophomonas maltophilia strain IAM 12423 (MN240936) (Fig.1). The 16S rRNA gene sequence of strain EPS was deposited to NCBI GenBank with accession number (OK584766). Cd tolerance by the strain Cd concentration was significantly ( f- value= 20.759; p -value= 0.00001) effected on the growth of the strain. It was observed that the strain could grow until 200 mg mL -1 Cd 2+ , above this concentration its growth was dramatically declined. Cd- adsorption potential of the strain The Cd- adsorption efficiency by strain EPS was measured for the whole culture (cells and supernatant containing EPS). It was observed that the Cd- adsorption efficiency was 95.42 % and 89.96 % in 50 and 100 mg L -1 Cd-supplemented culture media by strain EPS. Our findings are in agreement with Liaquat et al. (2020) investigation who reported that Stenotrophomonas maltophilia has remarkable Cd- adsorption potential under varying concentrations. Bacterial inoculation and antioxidant defense of safflower under Cd-stress Levels of antioxidants within the plant cell tend to fluctuate at cadmium exposure (Ali et al. 2019). The interaction between plants and microorganisms at biochemical, physiological and molecular levels largely directs plant responses toward abiotic stresses (Farrar et al. 2014; Meena et al. 2017). This crucial aspect considered as an interest gateway for scientists to search novel cost-effective and eco-friendly methods to alleviate the abiotic stresses in field grown plants. The application of bacteria to mitigate stress-induced negative impact in plants and their role to make plants tougher toward abiotic stresses have been documented (Panlada et al. 2013; Nadeem et al. 2014; Kaushal and Wani 2016; Rizvi and Khan 2018; Ghosh et al. 2022). In this study, the efect of S. maltophilia EPS inoculation on the antioxidant defense of safflower plants ( Carthamus tinctorius L.) exposed to different levels of Cd was investigated. Hydrogen peroxide (H 2 O 2 ) content As a result of many stresses, the cellular concentration of superoxide radicals increases, which are subsequently converted to hydrogen peroxide by mitochondrial manganese superoxide dismutase (Huseynova et al. 2015). Hydrogen peroxide is one of the major contributors causing oxidative damage to plant cell, leading to inhibition of plant growth and development, or to death (Hung et al. 2005; Hossain et al. 2015). In the current work, it was found that the inoculation of safflower with S. maltophilia EPS significantly reduced the accumulation of H 2 O 2 in the plant leaves under all tested Cd concentrations compared with control plants (Fig.2). Non-enzymatic antioxidants levels The non-enzymatic antioxidants like phenolic compounds, flavonoids, ascorbate as well as carotenoids considered as the half of the antioxidant machinery of the plant cell (Das and Roychoudhury 2014). They play a vital role in the plant cell through protecting the cell components from oxidative damage as well as improving plant growth and development via modifying cellular processes such as mitosis, cell elongation, senescence and cell death (de Pinto and De Gara 2004). In the present study, the total phenolics significantly increased ( f = 9.11; p = 0.0129) with increasing Cd concentration in strain EPS- inoculated plants comparing to control plants (Fig. 3 a). Phenolics are better and more efficient antioxidant due to the presence of hydroxyl ions in their structure that can chelate metal ions, trap active oxygen species as well as inhibit lipid peroxidation (Michalak 2006; Ali et al. 2019). Flavonoids are secondary antioxidants with variable phenolic structures that act as reactive oxygen species (ROS) scavengers (Fini et al. 2011; Das and Roychoudhury 2014). Significantly, the inoculation with strain EPS enhanced the total flavonoids content at all the tested Cd concentrations (Fig. 3 b). The content of total flavonoids was increased in inoculated safflower plants by 38.9 and 49.4 % over the control plants at Cd concentrations of 50 and 100 mg L -1 respectively. Carotenoids are lipophilic antioxidants in the plant plastids. They prevent oxidative damage and protect photosynthetic apparatus via detoxifying multiple forms of ROS (McElroy and Kopsell 2009). It was observed that the content of carotenoids of control plants subjected to Cd treatments was remarkably decreased (Fig.3 c). This agreed with the findings of Shi et al. (2010) who reported that Cd exposure resulted in a decrease of carotenoids contents of safflower plants. This may be attributed to Cd-induced decrease of the photosynthetic rate (Mobin and Khan 2007; Shi et al. 2010). In contrast to the control plants, the contents of carotenoids of inoculated plants were significantly increased ( f = 12.375; p = 0.0055) at all tested Cd levels (Fig.3 c). Thus the inoculation with strain EPS significantly improved the quantities of carotenoids antioxidants of safflower plants under Cd stress. In the present study, it was found that the total antioxidant capacity of the inoculated plants was increased by 78.1 and 34 % over the control plants at 50 and 100 mg L -1 Cd respectively (Fig.3 d). Total antioxidant capacity was strongly correlated with total phenolics and total flavonoids contents. The positive correlations between total phenolics, total flavonoids and antioxidant activities were reported by other researchers (Gouveia and Castilho 2011; Contreras-Calderón et al. 2011; Aryal et al. 2019; Santos and MagalhÃes 2020; Butkeviciute et al. 2022). Enzymatic antioxidants levels Plants possess multiple antioxidative enzymes including catalase (CAT), guaiacol peroxidase (POX), Ascorbate peroxidase (APX) and superoxide dismutase (SOD) that alleviate oxidative stress and maintain redox homeostasis through catalyting the transformation of ROS into stable nontoxic molecules (Sáez and Están-Capell 2014). In the current study, no significant difference ( f = 1.7256; p = 0.218) was observed in CAT activity between inoculated and control plants (Fig.4 a). On the other hand, the inoculation with strain EPS significantly ( p < 0.05) enhanced the activities of POX, APX and SOD at all the tested Cd levels (Fig. 4 b, c, d). POX activity upon strain EPS inoculation was found to be increased by 20.6 % to 29.6 % under Cd stress compared with the control plants. The activities of APX and SOD of safflower plants were improved upon strain EPS inoculation by 40.5 to 109.9 % and 96.9 to 124.6 % over the control plants under Cd stress respectively. Conclusion The output of the present work is that the inoculation of strain EPS into safflower seeds protects plants from Cd-induced oxidative stress through adsorption as well as increasing the levels of antioxidant compounds and enhancing the activities of antioxidant enzymes. This study provides an eco-friendly and safety method for alleviating Cd-stress in plants that can guarantee safe agricultural productivity in Cd-contaminated fields. Declarations Funding This research did not receive any specific grant from funding agencies in the public, commercial, or not-for-profit sectors. CRediT authorship contribution statement Noura Sh. A. Hagaggi: Conceptualization, Methodology, Software, Formal analysis, Writing- Original draft preparation. Usama M. Abdul- Raouf: Methodology, Investigation, Supervision, writing- Reviewing and Editing. Declaration of Competing Interest The authors declare that they have no competing financial interests or personal relationships that could have appeared to influence the work reported in this paper. Acknowledgment We introduce our sincere thanks and gratitude to the Botany Department, Faculty of Science, Aswan University for supporting and providing the requirements of scientific research. References Ali M A, Fahad S, Haider I, Ahmed N, Ahmad S, Hussain S, Arshad M (2019) Oxidative stress and antioxidant defense in plants exposed to metal/metalloid toxicity. In Reactive oxygen, nitrogen and sulfur species in plants: production, metabolism, signalling and defense mechanisms, 353–370. NJ, USA: Wiley and Sons. Aryal S, Baniya M K, Danekhu K, Kunwar P, Gurung R, Koirala N (2019) Total Phenolic Content, Flavonoid Content and Antioxidant Potential of Wild Vegetables from Western Nepal. Plants (Basel, Switzerland), 8(4): 96. 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DOI: 10.1007/s11356-016-6436-4 Romero-Puertas, M C, Rodríguez‐Serrano M, Corpas F J, Gomez, M D, Del Rio L A, Sandalio L M (2004) Cadmium‐induced subcellular accumulation of O 2 and H 2 O 2 in pea leaves. Plant Cell Environ 27 (9): 1122–1134 Sáez G T, Están-Capell N (2014) Antioxidant Enzymes. In: Schwab M. (eds) Encyclopedia of Cancer. Springer, Berlin, Heidelberg. DOI: 10.1007/978-3-662-46875-3_7210 Santos W N L D, MagalhÃes B E A (2020) Phenolic content and antioxidant capacity of infusions herbs: Optimization of phenolic extraction and HPLC-DAD method. An Acad Bras Cienc 92(3): e20190646. DOI: 10.1590/0001-3765202020190646 Senthilkumar M, Amaresan N, Sankaranarayanan A (2021) Estimation of Ascorbate Peroxidase (APX). In: Plant-Microbe Interactions. Springer Protocols Handbooks. Humana, New York, NY. DOI: 10.1007/978-1-0716-1080-0_30 Shi G, Liu C, Cai Q, Liu Q, Hou C (2010) Cadmium accumulation and tolerance of two safflower cultivars in relation to photosynthesis and antioxidative enzymes. Bull Environ Contam Toxicol 85(3): 256–263. DOI: 10.1007/s00128-010-0067-0 Singleton V L, Orthofer R, Lamuela-Raventós R M (1999) Analysis of total phenols and other oxidation substrates and antioxidants by means of folin-ciocalteu reagent. In: Packer L (ed) Methods in enzymology: oxidants and antioxidants Part A, vol 299. Academic Press, London, 152–178 Sytar O, Kumar A, Latowski D, Kuczynska P, Strzałka K, Prasad M N V (2013) Heavy metal-induced oxidative damage, defense reactions, and detoxification mechanisms in plants. Acta Physiol Plant 35(4): 985–999 Tirry N, Tahri Joutey N, Sayel H, Kouchou A, Bahafid W, Asri M, et al. (2018) Screening of plant growth promoting traits in heavy metals resistant bacteria: prospects in phytoremediation. J Genet Eng Biotechnol 16 (2): 613–619. DOI: 10.1016/j.jgeb.2018.06.004 Tran T A, Popova L P (2013) Functions and toxicity of cadmium in plants: recent advances and future prospects. Tur J Bot 37:1–13 Van Rossun M W P C, Alberda M, Van Der Plas L H W (1997) Role of oxidative damage in tulip bulb scale micropropagation. Plant Sci 130: 207–216 Vashishth A, Khanna S (2015) Toxic heavy metals tolerance in bacterial isolates based on their inducible mechanism. Int J Novel Res Life Sci 2: 34–41. DOI: 10.21776/ub.rjls.2015.002.01.5 Velikova V, Yordanov I, Edreva A (2000) Oxidative stress and some antioxidant systems in acid rain treated bean plants, protective role of exogenous polyamines. Plant Sci 151: 59–66 Vincent J M (1970) "A Manual for the Practical Study of the Root-nodule Bacteria”. IBP15. Blackwell Scientific Publications, Oxford and Edinburgh. U.K. Wasay S A, Barrington S F, Tokunaga S (1998) Using Aspergillus niger to bioremediate soils contaminated by heavy metals. Bioremediat J 2 (3–4): 183–190 Weiss E (2000) Oilseed crops. Second Addition. Blackwell Science, London. Zengin F K, Munzuroglu O (2005) Effects of some heavy metals on content of chlorophyll, proline and some antioxidant chemicals in bean (Phaseolus vulgaris L.) seedlings. Acta Biol Crac Ser Bot 47(2): 157–164 Additional Declarations No competing interests reported. Cite Share Download PDF Status: Under Review Version 1 posted Editorial decision: Major revision 02 May, 2022 Reviews received at journal 19 Apr, 2022 Reviewers agreed at journal 18 Apr, 2022 Reviewers agreed at journal 12 Apr, 2022 Reviewers invited by journal 12 Apr, 2022 Editor assigned by journal 12 Apr, 2022 Submission checks completed at journal 09 Apr, 2022 First submitted to journal 08 Apr, 2022 You are reading this latest preprint version Research Square lets you share your work early, gain feedback from the community, and start making changes to your manuscript prior to peer review in a journal. As a division of Research Square Company, we’re committed to making research communication faster, fairer, and more useful. We do this by developing innovative software and high quality services for the global research community. Our growing team is made up of researchers and industry professionals working together to solve the most critical problems facing scientific publishing. Also discoverable on Platform About Our Team In Review Editorial Policies Advisory Board Help Center Resources Author Services Accessibility API Access RSS feed Manage Cookie Preferences © Research Square 2026 | ISSN 2693-5015 (online) Privacy Policy Terms of Service Do Not Sell My Personal Information {"props":{"pageProps":{"initialData":{"identity":"rs-1538673","acceptedTermsAndConditions":true,"allowDirectSubmit":false,"archivedVersions":[],"articleType":"Research Article","associatedPublications":[],"authors":[{"id":97377914,"identity":"95fe5174-fed3-4587-8302-3083c15367e2","order_by":0,"name":"Noura Sh. A. Hagaggi","email":"data:image/png;base64,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","orcid":"","institution":"Aswan University","correspondingAuthor":true,"prefix":"","firstName":"Noura","middleName":"Sh. A.","lastName":"Hagaggi","suffix":""},{"id":97377915,"identity":"c90b130d-56e0-4182-9d36-1fff802b2eae","order_by":1,"name":"Usama M. Abdul-Raouf","email":"","orcid":"","institution":"Aswan University","correspondingAuthor":false,"prefix":"","firstName":"Usama","middleName":"M.","lastName":"Abdul-Raouf","suffix":""}],"badges":[],"createdAt":"2022-04-08 20:59:03","currentVersionCode":1,"declarations":"","doi":"10.21203/rs.3.rs-1538673/v1","doiUrl":"https://doi.org/10.21203/rs.3.rs-1538673/v1","draftVersion":[],"editorialEvents":[],"editorialNote":"","failedWorkflow":false,"files":[{"id":20313848,"identity":"7181d9cb-9fe0-4d2b-b9b6-a071f8ddeaf5","added_by":"auto","created_at":"2022-04-13 19:55:45","extension":"jpg","order_by":1,"title":"Figure 1","display":"","copyAsset":false,"role":"figure","size":71977,"visible":true,"origin":"","legend":"\u003cp\u003eNeighbor-joining phylogenetic tree with 1000 bootstrap replication using MEGA X10.1.7\u0026nbsp;software displaying the relationship between strain EPS and the closely related members of genus \u003cem\u003eStenotrophomonas\u003c/em\u003e derived from NCBI reference sequence database.\u0026nbsp;\u0026nbsp;\u003cstrong\u003e\u0026nbsp;\u0026nbsp;\u003c/strong\u003e\u003c/p\u003e","description":"","filename":"Fig1.jpg","url":"https://assets-eu.researchsquare.com/files/rs-1538673/v1/01ebe32018d7ad7bc3b89a72.jpg"},{"id":20313849,"identity":"2516122b-cd11-41d0-8d67-bdddfa314eb7","added_by":"auto","created_at":"2022-04-13 19:55:45","extension":"jpg","order_by":2,"title":"Figure 2","display":"","copyAsset":false,"role":"figure","size":42289,"visible":true,"origin":"","legend":"\u003cp\u003eDifferences in hydrogen peroxide (H\u003csub\u003e2\u003c/sub\u003eO\u003csub\u003e2\u003c/sub\u003e) content between inoculated and control safflower plants at different Cd-concentrations.\u0026nbsp;\u0026nbsp;\u003c/p\u003e","description":"","filename":"Fig2.jpg","url":"https://assets-eu.researchsquare.com/files/rs-1538673/v1/4b4305f1b829fe879eef3f34.jpg"},{"id":20313851,"identity":"6a64c3bb-ce62-4aa2-a20d-df66feb200c2","added_by":"auto","created_at":"2022-04-13 19:55:46","extension":"jpg","order_by":3,"title":"Figure 3","display":"","copyAsset":false,"role":"figure","size":88799,"visible":true,"origin":"","legend":"\u003cp\u003eVariation of (a) total phenolics, (b) flavonoids , (c) Carotenoids and (d) total antioxidant capacity (mg/g FW) under different Cd-concentrations. Data are means ± SEs of three independent replicates (n = 3). Different letters indicate significant differences (p ≤ 0.05) between inoculated and control plants according to Tukey's HSD test.\u0026nbsp;\u003c/p\u003e\u003cp\u003e\u003cbr\u003e\u003c/p\u003e","description":"","filename":"Fig3.jpg","url":"https://assets-eu.researchsquare.com/files/rs-1538673/v1/30aab3cb22eab313b5ac86bb.jpg"},{"id":20313850,"identity":"4d29ab60-23e1-4f8c-a2ac-b42891066ba5","added_by":"auto","created_at":"2022-04-13 19:55:45","extension":"jpg","order_by":4,"title":"Figure 4","display":"","copyAsset":false,"role":"figure","size":73726,"visible":true,"origin":"","legend":"\u003cp\u003eAntioxidant enzyme activities of\u003cstrong\u003e \u003c/strong\u003e(a)\u003cstrong\u003e \u003c/strong\u003ecatalase (CAT), (b) guaiacol peroxidase (POX), (c) Ascorbate peroxidase (APX) and (d) superoxide dismutase (SOD)\u003cstrong\u003e \u003c/strong\u003erepresenting inoculated and control plants under different Cd-concentrations. Different letters indicate significant differences (p ≤ 0.05) between inoculated and control plants according to Tukey's HSD test.\u003c/p\u003e\u003cp\u003e\u003cbr\u003e\u003c/p\u003e","description":"","filename":"Fig4.jpg","url":"https://assets-eu.researchsquare.com/files/rs-1538673/v1/aa25548a5ea25fc8ab4bb74e.jpg"},{"id":20313852,"identity":"1f69917b-5a0b-40e7-bef7-0b00e18c9ddb","added_by":"auto","created_at":"2022-04-13 19:55:48","extension":"pdf","order_by":0,"title":"","display":"","copyAsset":false,"role":"manuscript-pdf","size":668814,"visible":true,"origin":"","legend":"","description":"","filename":"manuscript.pdf","url":"https://assets-eu.researchsquare.com/files/rs-1538673/v1/a4d4e857-48fe-4425-be0b-46f56fbdb9c5.pdf"}],"financialInterests":"No competing interests reported.","formattedTitle":"The endophyte Stenotrophomonas maltophilia EPS modulates endogenous antioxidant defense in safflower (Carthamus tinctorius L.) under cadmium stress","fulltext":[{"header":"Introduction","content":"\u003cp\u003eOver wide world, heavy metals accumulation in agricultural soils is a serious problem threats crop production (He et al. \u003cspan citationid=\"CR26\" class=\"CitationRef\"\u003e2015\u003c/span\u003e; Rizwan et al. \u003cspan citationid=\"CR55\" class=\"CitationRef\"\u003e2016a\u003c/span\u003e). Heavy metals are among the most main causes of environmental stresses. Overaccumulation of heavy metals in the soils causes dangerous phytotoxicity that can store in plants and easy transmit through the food chain resulting in negatively impact on human and animal health (Fryzova et al. \u003cspan citationid=\"CR20\" class=\"CitationRef\"\u003e2017\u003c/span\u003e). Hyperlevels of heavy metals alter normal plant functions and metabolism causing repression of vital processes such as photosynthesis, respiration, and enzymatic activities (Hossain et al. \u003cspan citationid=\"CR29\" class=\"CitationRef\"\u003e2012\u003c/span\u003e). On the other hand, high levels of heavy metals can induce excess generation of reactive oxygen species (ROS) as well as cytotoxic compounds, leading to oxidative stress via demolishing the equilibrium between prooxidants and antioxidants within the plant cells (Zengin and Munzuroglu \u003cspan citationid=\"CR71\" class=\"CitationRef\"\u003e2005\u003c/span\u003e; Hossain et al. \u003cspan citationid=\"CR29\" class=\"CitationRef\"\u003e2012\u003c/span\u003e; Sytar et al. \u003cspan citationid=\"CR62\" class=\"CitationRef\"\u003e2013\u003c/span\u003e). This results in cellular damage as well as decreasing plant productivity (Raja et al. \u003cspan citationid=\"CR53\" class=\"CitationRef\"\u003e2017\u003c/span\u003e).\u003c/p\u003e \u003cp\u003eCadmium (Cd) is non-essential element for living organisms, and it is highly toxic to plants and animals even at very low concentrations (Dai et al. \u003cspan citationid=\"CR11\" class=\"CitationRef\"\u003e2012\u003c/span\u003e). Cadmium mainly originates from industrial processes and phosphate fertilizers, releases into agricultural lands and has long biological half-life (Gill et al. \u003cspan citationid=\"CR22\" class=\"CitationRef\"\u003e2013\u003c/span\u003e). In plants, the exposure to cadmium induces numerous hazards physiological and growth changes as well as oxidative stress by generating ROS, that react with lipids, proteins, pigments and nucleic acids in the plant cell, leading to cellular damage and consequently decreasing productivity (Romero-Puertas et al. \u003cspan citationid=\"CR56\" class=\"CitationRef\"\u003e2004\u003c/span\u003e). Furthermore, cadmium also can transfer into human via food chain and can result in kidney, bone and lung diseases (Bernard \u003cspan citationid=\"CR5\" class=\"CitationRef\"\u003e2008\u003c/span\u003e).\u003c/p\u003e \u003cp\u003eTraditional remediation techniques for heavy metal-contaminated soils are expensive and destructive to environment (Meagher \u003cspan citationid=\"CR44\" class=\"CitationRef\"\u003e2000\u003c/span\u003e). Therefore, scientists and engineers intensify their efforts to find cost effective and safe technologies (Boyajian and Carreira \u003cspan citationid=\"CR6\" class=\"CitationRef\"\u003e1997\u003c/span\u003e; Wasay et al. \u003cspan citationid=\"CR69\" class=\"CitationRef\"\u003e1998\u003c/span\u003e). Most of plant associated microorganisms are metal resistant, whose application in heavy metal contaminated soils can improve metal immobilization in soils and plant biomass (Ma et al. \u003cspan citationid=\"CR42\" class=\"CitationRef\"\u003e2011\u003c/span\u003e; Ma et al. \u003cspan citationid=\"CR41\" class=\"CitationRef\"\u003e2016\u003c/span\u003e).\u003c/p\u003e \u003cp\u003eDespite that the applications of some potential bacterial strains to remediate soils contaminated with heavy metals have been reported, it is urgent to search a new microbial resources that can be used efficiently in heavy metals remediation (Tirry et al. \u003cspan citationid=\"CR63\" class=\"CitationRef\"\u003e2018\u003c/span\u003e).\u003c/p\u003e \u003cp\u003eSafflower (\u003cem\u003eCarthamus tinctorius\u003c/em\u003e L.) is herbaceous annual plant belongs to family Asteraceae. It is cultivated from prehistoric times throughout many areas with temperate climates over the world including southern Asia, China, India, Iran and Egypt (Dordas and Sioulas \u003cspan citationid=\"CR15\" class=\"CitationRef\"\u003e2008\u003c/span\u003e; Weiss \u003cspan citationid=\"CR70\" class=\"CitationRef\"\u003e2000\u003c/span\u003e). Safflower is commercially used for vegetable oil extraction, as well as in the traditional medicine for the treatment of rheumatism, paralysis, vitiligo, psoriasis and mouth ulcers (Delshad et al. \u003cspan citationid=\"CR14\" class=\"CitationRef\"\u003e2018\u003c/span\u003e). Moreover, it has numerous pharmacological activities i.e, antioxidant, analgesic, anti-inflammatory and antidiabetic activities (Asgarpanah and Kazemivash \u003cspan citationid=\"CR3\" class=\"CitationRef\"\u003e2013\u003c/span\u003e).\u003c/p\u003e \u003cp\u003eIt has been reported that safflower plants can accumulate high levels of Cd in their roots and leaves (Shi et al. \u003cspan citationid=\"CR60\" class=\"CitationRef\"\u003e2010\u003c/span\u003e; Namdjoyan et al. \u003cspan citationid=\"CR50\" class=\"CitationRef\"\u003e2011\u003c/span\u003e). Although, some scientific data exists on the antioxidant defense mechanisms in response to cadmium stress in safflower cultivars (Namdjoyan et al. \u003cspan citationid=\"CR50\" class=\"CitationRef\"\u003e2011\u003c/span\u003e), to our knowledge, there is no study dealing with alleviation of Cd- induced oxidative stress in safflower by using bacteria. Therefore, the present work was designed to investigate the potentiality of the endophytic bacterium \u003cem\u003eStenotrophomonas maltophilia\u003c/em\u003e strain EPS to alleviate Cd-induced oxidative stress in safflower plants.\u003c/p\u003e"},{"header":"Materials And Methods","content":"\u003cp\u003e\u003cstrong\u003eIsolation and identification of endophytic bacteria\u003c/strong\u003e\u003c/p\u003e\n\u003cp\u003eHealthy fresh roots of common bean plants (\u003cem\u003eVigna unguiculata\u003c/em\u003e L.) were collected in sterile plastic bags from Aswan University greenhouse. Immediately nodules were surface- sterilized using 70 % ethanol (30 sec) followed by 5 % sodium hypochlorite (3 min) and then washed three times with sterilized distilled water (Vincent 1970). Under aseptic conditions, nodules were crushed in a test tube contained one mL of sterilized saline solution. Loopful of the obtained suspension was streaked on the surface of tryptic soy agar and nutrient agar plates. Plates were incubated at 37 \u003csup\u003eo\u003c/sup\u003eC for 72 h for the appearance of colonies.\u0026nbsp;\u003c/p\u003e\n\u003cp\u003eThe ribosomal (16S rRNA) gene of the selected strain was amplified using 27F and 1492R primers (Frank et al. 2008) in Applied Biotechnology lab at Ismailia, Egypt. PCR product was sent to SolGent Co., Ltd., South Korea for sequencing. Then, the similarity of the obtained sequence was evaluated based on BLAST outputs using NCBI reference sequence database. Neighbor-joining phylogenetic tree of the strain was constructed using MEGA X 10.1.7 software (Kumar et\u0026nbsp;al. 2018).\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003eCd tolerance of the strain\u003c/strong\u003e\u003c/p\u003e\n\u003cp\u003eMaximum tolerable concentration (MTC) of cadmium by the strain was determined according to the method of Vashishth and Khanna (2015), with slight modification. Briefly, 10 mL of yeast extract-mannitol broth (YMB) in glass tubes was supplemented with different concentrations of CdCl\u003csub\u003e2\u003c/sub\u003e i.e., 0 (control), 50, 100, 150, 200, 250 and 300 mg L\u003csup\u003e-1\u003c/sup\u003e. 10 mL of YMB without CdCl\u003csub\u003e2\u0026nbsp;\u003c/sub\u003ewas used as control.\u003csub\u003e\u0026nbsp;\u003c/sub\u003eTubes were inoculated with 1 mL of inoculum (10\u003csup\u003e7\u003c/sup\u003e CFUmL\u003csup\u003e-1\u003c/sup\u003e), and incubated for 48 h at 28 \u003csup\u003eo\u003c/sup\u003eC and 150 rpm. The optical density (OD) was measured at 600 nm. \u0026nbsp;The highest concentration of cadmium (CdCl\u003csub\u003e2\u003c/sub\u003e) that allowed visible bacterial growth after 48 h of incubation was considered as the maximum tolerable concentration (MTC). \u0026nbsp;\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003eEvaluation of Cd-\u0026nbsp;\u003c/strong\u003e\u003cstrong\u003eadsorption potential\u003cspan dir=\"RTL\"\u003e\u0026nbsp;\u003c/span\u003eof the strain\u0026nbsp;\u003c/strong\u003e\u003c/p\u003e\n\u003cp\u003eThe ability of the whole culture of the present strain (cells and supernatant) for adsorping cadmium was evaluated using the method of Du et al. (2016 b). 100 mL of the whole culture broth contained 50 and 100 mg L\u003csup\u003e-1\u003c/sup\u003e of CdCl\u003csub\u003e2\u003c/sub\u003e was shaken at 120 rpm and 28 \u003csup\u003eo\u003c/sup\u003eC for 24 h. Cells were then removed by centrifugation. Concentration of the residual, non-adsorbed metal ion in the solution was estimated by atomic absorption spectrophotometer (Thermo Scientific\u0026trade; iCE\u0026trade; 3000). Experiment was performed in triplicate. The adsorption efficiency (%) was calculated according to the following formula:\u0026nbsp;\u003c/p\u003e\n\u003cp\u003e\u003cimg 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\"\u003e\u003c/p\u003e\n\u003cp\u003ewhere Cdi and Cde are the concentration of initial and equilibrium Cd ion in the solution (mgL\u003csup\u003e-1\u003c/sup\u003e) respectively.\u0026nbsp;\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003eSeed inoculation and pot experiment\u003c/strong\u003e\u003c/p\u003e\n\u003cp\u003eSeeds of safflower (cv. Giza-1) were obtained from Faculty of Agriculture and Natural Resources, Aswan University. Seeds were surface sterilized with 70 % ethanol for 3 min, rinsed three times with sterilized distilled water. Seeds thereafter were soaked in a freshly prepared bacterial suspension (1\u0026times;10\u003csup\u003e8\u003c/sup\u003e CFU mL\u003csup\u003e-1\u003c/sup\u003e) for 1 h, and left to dry before sowing. Seeds used for control were soaked in sterilized distilled water.\u0026nbsp;\u003c/p\u003e\n\u003cp\u003eSeeds were sown in pots containing an autoclaved mixture of clay and sand (1:1 w/w), with maintaining field capacity at 90 %. Pots were kept under normal climatic conditions. After three weeks of sowing, five homogenous plants in each pot were subjected to three Cd treatments including 0 (control), 50 and 100 mg L\u003csup\u003e-1\u003c/sup\u003e of CdCl\u003csub\u003e2\u003c/sub\u003e. After three weeks of cadmium exposure, healthy expanded leaf samples were collected, frozen and then used for measuring the defensive non-enzymatic and enzymatic antioxidant activities. The experiment was repeated twice.\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003eEstimation of\u0026nbsp;\u003c/strong\u003e\u003cstrong\u003ehydrogen peroxide (H\u003csub\u003e2\u003c/sub\u003eO\u003csub\u003e2\u003c/sub\u003e) content\u003c/strong\u003e\u003c/p\u003e\n\u003cp\u003eTo evaluate the H\u003csub\u003e2\u003c/sub\u003eO\u003csub\u003e2\u0026nbsp;\u003c/sub\u003econtent of the leaves, the method of Velikova et al. (2000) was followed. One gram of fresh leaves was homogenated in 10 mL trichloroacetic acid (0.1 %) using a mortar and pestle, and then centrifuged. To 0.5 mL of the supernatant, 0.5 mL of potassium phosphate buffer (pH 7.0) and 1 mL of 1 M KI were added. The mixture was vortexed, and the absorbance was read at 390 nm. A calibration curve of different concentrations (\u0026micro;mol) of 30 % (v/v) H\u003csub\u003e2\u003c/sub\u003eO\u003csub\u003e2\u003c/sub\u003e was used as standard. \u0026nbsp;\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003eAssessments of\u0026nbsp;\u003c/strong\u003e\u003cstrong\u003enon-enzymatic\u0026nbsp;\u003c/strong\u003e\u003cstrong\u003eantioxidants\u003c/strong\u003e\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003eTotal phenolics\u003c/strong\u003e\u003c/p\u003e\n\u003cp\u003eThe Folin-Ciocalteu assay described by Singleton et al. (1999) was followed to determine the total phenolic compounds in the leaves extracts. Absorbance was read at 700 nm, and the content of total phenolics was expressed as mg gallic acid equivalents per gram of fresh weight using gallic acid as a reference.\u0026nbsp;\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003eTotal flavonoids\u003c/strong\u003e\u003cstrong\u003e\u0026nbsp;\u003c/strong\u003e\u003c/p\u003e\n\u003cp\u003eAluminum chloride method according to Chang et al. (2002) was used for quantifying the total contents of flavonoids of the extracts. The absorbance was recorded at wavelength 510 nm. The concentration of flavonoids was calculated from quercetin calibration curve as mg quercetin equivalents per gram of fresh weight.\u0026nbsp;\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003eTotal carotenoids\u0026nbsp;\u003c/strong\u003e\u003c/p\u003e\n\u003cp\u003ePigments were extracted\u003cspan dir=\"RTL\"\u003e\u0026nbsp;\u003c/span\u003efrom fresh leaves and their contents were estimated as described by Lichtenthaler and Wellburn (1983). One gram of fresh leaves was macerated in \u0026nbsp;80 % acetone, the supernatant was filtered and makeup to 50 mL with the solvent. The total contents of chlorophylls a (Chl a), chlorophylls b (Chl b) and carotenoids were measured by reading the absorbance at wavelengths 646, 663 and 440.5 nm respectively. The content of each pigment was calculated in mg per gram of fresh weight using the following equations:\u0026nbsp;\u003c/p\u003e\n\u003cp\u003eChl a (mg g f.wt.\u003csup\u003e\u003cspan dir=\"RTL\"\u003e-\u003c/span\u003e1\u003c/sup\u003e) = (12.21\u0026times;A\u003csub\u003e663\u003c/sub\u003e) - (2.81\u0026times;A\u003csub\u003e646\u003c/sub\u003e) \u0026nbsp; \u0026nbsp; \u0026nbsp; \u0026nbsp; \u0026nbsp; \u0026nbsp; \u0026nbsp; \u0026nbsp; \u0026nbsp; \u0026nbsp; \u0026nbsp; \u0026nbsp; \u0026nbsp; \u0026nbsp; \u0026nbsp; \u0026nbsp; \u0026nbsp;\u0026nbsp;\u003c/p\u003e\n\u003cp\u003eChl b (mg g f.wt.\u003csup\u003e\u003cspan dir=\"RTL\"\u003e-\u003c/span\u003e1\u003c/sup\u003e) = (20.13\u0026times;A\u003csub\u003e646\u003c/sub\u003e) \u0026ndash; (5.03\u0026times;A\u003csub\u003e663\u003c/sub\u003e)\u003c/p\u003e\n\u003cp\u003eCarotenoids (mg g f.wt.\u003csup\u003e\u003cspan dir=\"RTL\"\u003e-\u003c/span\u003e1\u003c/sup\u003e) = (4.69\u0026times;A\u003csub\u003e440.5\u003c/sub\u003e) - 0.268\u0026times; (Chla + Chlb) \u0026nbsp; \u0026nbsp;\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003eTotal antioxidant capacity\u003c/strong\u003e\u003c/p\u003e\n\u003cp\u003eTotal antioxidant capacity of the ethanolic extracts of the leaves was measured per gram of fresh weight as mg ascorbic acid equivalents using ascorbic acid standard curve, according to phosphomolybdnum assay (Prieto et al. 1999). \u0026nbsp; \u0026nbsp; \u0026nbsp; \u0026nbsp; \u0026nbsp; \u0026nbsp; \u0026nbsp; \u0026nbsp; \u0026nbsp;\u0026nbsp;\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003eAssessments of enzymatic antioxidants \u0026nbsp;\u003c/strong\u003e\u003c/p\u003e\n\u003cp\u003eAntioxidant enzymes were extracted from fresh leaves according to Cavalcanti et al. (2004) with slight modification. One gram of fresh leaves was homogenized using a mortar in 10 mL of extraction buffer containing 0.2 M of potassium phosphate buffer (pH 7.2), 0.1 mM EDTA and 1 mM phenylmethylsulfonyl fluoride as proteinase inhibitor. The homogenate was filtered. The obtained filtrate was used for enzymatic assays. \u0026nbsp;\u0026nbsp;\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003eCatalase (CAT) activity\u0026nbsp;\u003c/strong\u003e\u003c/p\u003e\n\u003cp\u003eCatalase activity was estimated by the method of Kato and Shimizu (1987). To 3 mL of the reaction mixture containing 50 mM potassium phosphate buffer (pH 7.0) and 20 mM H\u003csub\u003e2\u003c/sub\u003eO\u003csub\u003e2\u003c/sub\u003e,\u0026nbsp;100 \u0026micro;l of enzymatic extract was added. The decrease in H\u003csub\u003e2\u003c/sub\u003eO\u003csub\u003e2\u003c/sub\u003e was followed as decline in optical density at 240 nm. Catalase activity was calculated with the extinction coefficient of H\u003csub\u003e2\u003c/sub\u003eO\u003csub\u003e2\u003c/sub\u003e (40 mM\u003csup\u003e\u0026minus;1\u003c/sup\u003e cm\u003csup\u003e\u0026minus;1\u003c/sup\u003e), and expressed as 1\u0026mu;mol of H\u003csub\u003e2\u003c/sub\u003eO\u003csub\u003e2\u003c/sub\u003e decomposed per minute under assay conditions.\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003eGuaiacol peroxidase\u0026nbsp;\u003c/strong\u003e\u003cstrong\u003e(POX) activity\u003c/strong\u003e\u003c/p\u003e\n\u003cp\u003eThe activity of guaiacol peroxidase enzyme was determined following the method of Kim and Yoo (1996). Briefly, the reaction mixture contained 0.2 mL of\u0026nbsp;enzyme extract, 0.8 mL of phosphate buffer (0.2 M, pH 7.2), 1 mL of guaiacol (15 mM) and 1 mL of hydrogen peroxide (3 mM) was incubated for 10 min at 30 \u0026deg;C.\u0026nbsp;Reaction was terminated using 0.5 mL of H\u003csub\u003e2\u003c/sub\u003eSO\u003csub\u003e4\u0026nbsp;\u003c/sub\u003e(5 %), and the absorbance was read at 470 nm.\u0026nbsp;POX activity was calculated using the extinction coefficient of oxidation product (tetraguaiacol), (\u0026epsilon;470= 26.6 mM cm\u003csup\u003e-1\u003c/sup\u003e) as follow:\u0026nbsp;\u003c/p\u003e\n\u003cp\u003eU/mL = [Change in absorbance min\u003csup\u003e\u0026minus;1\u003c/sup\u003e\u0026times; Reaction mixture volume (mL) \u0026times; Dilution factor]/ [\u0026epsilon;470\u0026times; Enzyme extract volume (mL)] \u0026nbsp;\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003eAscorbate peroxidase (APX) activity\u003c/strong\u003e\u003c/p\u003e\n\u003cp\u003eAscorbate peroxidase activity was evaluated according to Senthilkumar et al. (2021). To 0.8 mL of a reaction mixture contained potassium phosphate buffer (50 mM), ascorbic acid (0.5 mM), H\u003csub\u003e2\u003c/sub\u003eO\u003csub\u003e2\u003c/sub\u003e (1.0 mM) and EDTA (0.1 mM), 0.2 mL of the enzyme extract was added. After 30 s the decrease in absorbance at 290 nm was followed up to 60 s with an interval of 15 s. One unit of enzyme activity was expressed as the amount of enzyme required to oxidize 1 \u0026mu;moL of ascorbic acid per minute with absorbance coefficient 2.8 mM cm at 290 nm.\u0026nbsp;\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003eSuperoxide dismutase (\u003c/strong\u003e\u003cstrong\u003eSOD\u003c/strong\u003e\u003cstrong\u003e) activity\u003c/strong\u003e\u003cstrong\u003e\u0026nbsp;\u003c/strong\u003e\u003c/p\u003e\n\u003cp\u003eSuperoxide dismutase activity was estimated according to Van Rossun et al. (1997). Three mL of reaction mixture contained 50 mM sodium phosphate buffer (pH 7.6), 0.1 mM EDTA, 50 mM sodium carbonate, 50 \u0026mu;M nitroblue tetrazolium (NBT), 10 \u0026mu;M riboflavin, 12 mM L-methionine and 100 \u0026mu;l of crude extract. Tubes contained the same reaction mixture without enzyme extract used as control. The tubes were placed under two 15\u0026thinsp;W fluorescent lamps for 15\u0026thinsp;min to start the reaction. The absorbance was recorded at 560\u0026thinsp;nm. One unit of SOD activity was defined as the amount of enzyme which reduced the absorbance to 50 % compared with the control. \u0026nbsp;\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003eStatistical analysis\u003c/strong\u003e\u003c/p\u003e\n\u003cp\u003eExperimental data were compared using one-way analysis of variance (ANOVA) with Tukey\u0026apos;s HSD test. Values were expressed as means \u0026plusmn; standard errors (SEs) of three biological replicates from two independent experiments. Differences were considered significant if p \u0026le; 0.05.\u003c/p\u003e"},{"header":"Results And Discussion","content":"\u003cp\u003eMetal toxicity and stress in plants triggering the excessive accumulation of ROS in mitochondria, chloroplast, and peroxisomes (Kochian et al. 2004), resulting in imbalance between the generation of ROS and antioxidant defense systems, that in turn causes oxidative stress to plants (Gupta et al. 2013). Oxidative stress disturbs physiological and metabolic processes of the plants leading to a limitation in plant growth, crop production and yield, and consequently causes massive agricultural loss (Tran and Popova 2013). Recently, plant root-associated bacteria are globally used for the amelioration of crop performance to encounter heavy metal contamination in agricultural soils \u0026nbsp;(Mitra et al. 2018b; He et al. 2020; Ghosh et al. 2022).\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003eIdentification of isolated strain\u003c/strong\u003e\u003c/p\u003e\n\u003cp\u003eThe selected strain was coded as EPS. The NCBI- BLAST analysis of strain EPS sequence showed closely similarity with percent identity of 100 % to \u003cem\u003eStenotrophomonas maltophilia\u003c/em\u003e strain IAM 12423 (MN240936) (Fig.1). The 16S rRNA gene sequence of strain EPS was deposited to NCBI GenBank with accession number (OK584766).\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003eCd tolerance by the strain\u0026nbsp;\u003c/strong\u003e\u003c/p\u003e\n\u003cp\u003eCd concentration was significantly (\u003cem\u003ef-\u003c/em\u003evalue= 20.759; \u003cem\u003ep\u003c/em\u003e-value= 0.00001) effected on the growth of the strain. It was observed that the strain could grow until 200 mg mL\u003csup\u003e-1\u0026nbsp;\u003c/sup\u003eCd\u003csup\u003e2+\u003c/sup\u003e, above this concentration its growth was dramatically declined.\u0026nbsp;\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003eCd-\u0026nbsp;\u003c/strong\u003e\u003cstrong\u003eadsorption potential\u003cspan dir=\"RTL\"\u003e\u0026nbsp;\u003c/span\u003e\u003c/strong\u003e\u003cstrong\u003eof the strain\u0026nbsp;\u003c/strong\u003e\u003c/p\u003e\n\u003cp\u003eThe Cd- adsorption efficiency by strain EPS was measured for the whole culture (cells and supernatant containing EPS). It was observed that the Cd- adsorption efficiency was 95.42 % and 89.96 % in 50 and 100 mg L\u003csup\u003e-1\u003c/sup\u003e Cd-supplemented culture media by strain EPS. Our findings are in agreement with Liaquat et al. (2020) investigation who reported that \u003cem\u003eStenotrophomonas maltophilia\u003c/em\u003e has remarkable Cd- adsorption potential under varying concentrations.\u0026nbsp;\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003eBacterial inoculation and antioxidant defense of safflower under Cd-stress\u003c/strong\u003e\u003c/p\u003e\n\u003cp\u003eLevels of antioxidants within the plant cell tend to fluctuate at cadmium exposure (Ali et al. 2019). The interaction between plants and microorganisms at biochemical, physiological and molecular levels largely directs plant responses toward abiotic stresses (Farrar et al. 2014; Meena et al. 2017). This crucial aspect considered as an interest gateway for scientists to search novel cost-effective and eco-friendly methods to alleviate the abiotic stresses in field grown plants. The application of bacteria to mitigate stress-induced negative impact in plants and their role to make plants tougher toward abiotic stresses have been documented (Panlada et al. 2013; Nadeem et al. 2014; Kaushal and Wani 2016; Rizvi and Khan 2018; Ghosh et al. 2022). In this study, the efect of \u003cem\u003eS. maltophilia\u003c/em\u003e EPS inoculation on the antioxidant defense of safflower plants (\u003cem\u003eCarthamus tinctorius\u003c/em\u003e L.) exposed to different levels of Cd was investigated.\u0026nbsp;\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003eHydrogen peroxide (H\u003csub\u003e2\u003c/sub\u003eO\u003csub\u003e2\u003c/sub\u003e) content \u0026nbsp;\u003c/strong\u003e\u003c/p\u003e\n\u003cp\u003eAs a result of many stresses, the cellular concentration of superoxide radicals increases, which are subsequently converted to hydrogen peroxide by mitochondrial manganese superoxide dismutase (Huseynova et al. 2015). Hydrogen peroxide is one of the major contributors causing oxidative damage to plant cell, leading to inhibition of plant growth and development, or to death (Hung et al. 2005; Hossain et al. 2015). In the current work, it was found that the inoculation of safflower with \u003cem\u003eS. maltophilia\u003c/em\u003e EPS significantly reduced the accumulation of H\u003csub\u003e2\u003c/sub\u003eO\u003csub\u003e2\u0026nbsp;\u003c/sub\u003ein the plant leaves under all tested Cd concentrations compared with control plants (Fig.2).\u0026nbsp;\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003eNon-enzymatic antioxidants levels\u003c/strong\u003e\u003c/p\u003e\n\u003cp\u003eThe non-enzymatic antioxidants like phenolic compounds, flavonoids, ascorbate as well as carotenoids considered as the half of the\u003cspan dir=\"RTL\"\u003e\u0026nbsp;\u003c/span\u003eantioxidant machinery\u003cspan dir=\"RTL\"\u003e\u0026nbsp;\u003c/span\u003eof the plant cell (Das and Roychoudhury 2014). They play a vital role in the plant cell through protecting the cell components from oxidative damage as well as improving plant growth and development via modifying cellular processes such as mitosis, cell elongation, senescence and cell death (de Pinto and De Gara 2004). In the present study, the total phenolics significantly increased (\u003cem\u003ef\u0026nbsp;\u003c/em\u003e= 9.11; \u003cem\u003ep\u003c/em\u003e = 0.0129) with increasing Cd concentration in strain EPS- inoculated plants comparing to control plants (Fig. 3 a). Phenolics are better and more efficient antioxidant due to the presence of hydroxyl ions in their structure that can chelate metal ions, trap active oxygen species as well as inhibit lipid peroxidation (Michalak 2006; Ali et al. 2019).\u003c/p\u003e\n\u003cp\u003eFlavonoids are secondary antioxidants with variable phenolic structures that act as reactive oxygen species (ROS) scavengers (Fini et al. 2011; Das and Roychoudhury 2014). Significantly, the inoculation with strain EPS enhanced the total flavonoids content at all the tested Cd concentrations (Fig. 3 b). The content of total flavonoids was increased in inoculated safflower plants by 38.9 and 49.4 % over the control plants at Cd concentrations of 50 and 100 mg L\u003csup\u003e-1\u003c/sup\u003e respectively. \u0026nbsp;\u0026nbsp;\u003c/p\u003e\n\u003cp\u003eCarotenoids are lipophilic antioxidants in the plant plastids. They prevent oxidative damage and protect photosynthetic apparatus via detoxifying multiple forms of ROS (McElroy and Kopsell 2009). It was observed that the content of carotenoids of control plants subjected to Cd treatments was remarkably decreased (Fig.3 c). This agreed with the findings of Shi et al. (2010) who reported that Cd exposure resulted in a decrease of carotenoids contents of safflower plants. This may be attributed to Cd-induced decrease of the photosynthetic rate (Mobin and Khan 2007; Shi et al. 2010). In contrast to the control plants, the contents of carotenoids of inoculated plants were significantly increased (\u003cem\u003ef\u003c/em\u003e = 12.375; \u003cem\u003ep\u003c/em\u003e= 0.0055) at all tested Cd levels (Fig.3 c). Thus the inoculation with strain EPS significantly improved the quantities of carotenoids antioxidants of safflower plants under Cd stress.\u0026nbsp;\u003c/p\u003e\n\u003cp\u003eIn the present study, it was found that the total antioxidant capacity of the inoculated plants was increased by 78.1 and 34 % over the control plants at 50 and 100 mg L\u003csup\u003e-1\u003c/sup\u003e\u0026nbsp; Cd respectively (Fig.3 d). Total antioxidant capacity was strongly correlated with total phenolics and total flavonoids contents. The positive correlations between total phenolics, total flavonoids and antioxidant activities were reported by other researchers (Gouveia and Castilho 2011; Contreras-Calder\u0026oacute;n et al. 2011; Aryal et al. 2019; Santos and Magalh\u0026Atilde;es 2020; Butkeviciute et al. 2022).\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003eEnzymatic antioxidants levels\u0026nbsp;\u003c/strong\u003e\u003c/p\u003e\n\u003cp\u003ePlants possess multiple antioxidative enzymes including catalase (CAT), guaiacol peroxidase (POX), Ascorbate peroxidase (APX) and superoxide dismutase (SOD) that alleviate oxidative stress and maintain redox homeostasis through catalyting the transformation of ROS into stable nontoxic molecules (S\u0026aacute;ez and Est\u0026aacute;n-Capell 2014). In the current study, no significant difference (\u003cem\u003ef\u003c/em\u003e = 1.7256; \u003cem\u003ep\u003c/em\u003e = 0.218) was observed in CAT activity between inoculated and control plants (Fig.4 a). On the other hand, the inoculation with strain EPS significantly (\u003cem\u003ep\u003c/em\u003e \u0026lt; 0.05) enhanced the activities of POX, APX and SOD at all the tested Cd levels (Fig. 4 b, c, d). POX activity upon strain EPS inoculation was found to be increased by 20.6 % to 29.6 % under Cd stress compared with the control plants. The activities of APX and SOD of safflower plants were improved upon strain EPS inoculation by 40.5 to 109.9 % and 96.9 to 124.6 % over the control plants under Cd stress respectively. \u0026nbsp;\u003c/p\u003e"},{"header":"Conclusion","content":"\u003cp\u003eThe output of the present work is that the inoculation of strain EPS into safflower seeds protects plants from Cd-induced oxidative stress through adsorption as well as increasing the levels of antioxidant compounds and enhancing the activities of antioxidant enzymes. This study provides an eco-friendly and safety method for alleviating Cd-stress in plants that can guarantee safe agricultural productivity in Cd-contaminated fields.\u003c/p\u003e"},{"header":"Declarations","content":"\u003cp\u003e\u003cstrong\u003eFunding\u003c/strong\u003e\u003c/p\u003e\n\u003cp\u003eThis research did not receive any specific grant from funding agencies in the public, commercial, or not-for-profit sectors.\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003eCRediT authorship contribution statement\u0026nbsp;\u003c/strong\u003e\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003eNoura Sh. A. Hagaggi:\u003c/strong\u003e Conceptualization, Methodology, Software, Formal analysis, Writing- Original draft preparation. \u003cstrong\u003eUsama M. Abdul- Raouf:\u003c/strong\u003e Methodology, Investigation, Supervision, writing- Reviewing and Editing.\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003eDeclaration of Competing Interest\u003c/strong\u003e\u003c/p\u003e\n\u003cp\u003eThe authors declare that they have no competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.\u0026nbsp;\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003eAcknowledgment\u003c/strong\u003e\u003c/p\u003e\n\u003cp\u003eWe introduce our sincere thanks and gratitude to the Botany Department, Faculty of Science, Aswan University for supporting and providing the requirements of scientific research.\u003c/p\u003e"},{"header":"References","content":"\u003col\u003e\u003cli\u003e\u003cspan\u003eAli M A, Fahad S, Haider I, Ahmed N, Ahmad S, Hussain S, Arshad M (2019) Oxidative stress and antioxidant defense in plants exposed to metal/metalloid toxicity. 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Acta Biol Crac Ser Bot 47(2): 157\u0026ndash;164\u003c/span\u003e\u003c/li\u003e\u003c/ol\u003e"}],"fulltextSource":"","fullText":"","funders":[],"hasAdminPriorityOnWorkflow":false,"hasManuscriptDocX":true,"hasOptedInToPreprint":true,"hasPassedJournalQc":"","hasAnyPriority":false,"hideJournal":false,"highlight":"","institution":"","isAcceptedByJournal":true,"isAuthorSuppliedPdf":false,"isDeskRejected":"","isHiddenFromSearch":false,"isInQc":false,"isInWorkflow":false,"isPdf":false,"isPdfUpToDate":true,"isWithdrawnOrRetracted":false,"journal":{"display":true,"email":"[email protected]","identity":"archives-of-microbiology","isNatureJournal":false,"hasQc":true,"allowDirectSubmit":false,"externalIdentity":"aomi","sideBox":"Learn more about [Archives of Microbiology](https://www.springer.com/journal/203)","snPcode":"203","submissionUrl":"https://submission.nature.com/new-submission/203/3","title":"Archives of Microbiology","twitterHandle":"","acdcEnabled":true,"dfaEnabled":true,"editorialSystem":"em","reportingPortfolio":"Springer Hybrid","inReviewEnabled":true,"inReviewRevisionsEnabled":false},"keywords":"Cadmium, Antioxidant, Safflower, Stenotrophomonas maltophilia ","lastPublishedDoi":"10.21203/rs.3.rs-1538673/v1","lastPublishedDoiUrl":"https://doi.org/10.21203/rs.3.rs-1538673/v1","license":{"name":"CC BY 4.0","url":"https://creativecommons.org/licenses/by/4.0/"},"manuscriptAbstract":"\u003cp\u003eCadmium (Cd) pollution in agricultural soils induces oxidative stress in plants that in turn is the foremost limiting factor for agricultural productivity. In past few decades, metal binding ability of microbes is of great interest as an emerging environmentally friendly technology that can be exploited to alleviate metal stress in plants. Considering these, in the present study an endophytic bacterium strain EPS has been isolated from the roots of common bean. The 16S rRNA sequence revealed its identity closely similar to \u003cem\u003eStenotrophomonas maltophilia\u003c/em\u003e. The strain showed tolerance to Cd stress up to 200 mg L\u003csup\u003e\u0026minus;\u0026thinsp;1\u003c/sup\u003e Cd\u003csup\u003e2+\u003c/sup\u003e. The inoculation of strain EPS in safflower seeds significantly enhanced the antioxidant defense of plants under Cd-stress conditions throught increasing the levels of antioxidant molecules like phenolics, flavonoids and carotenoids as well as improving the activities of the antioxidative enzymes including guaiacol peroxidase (POX), ascorbate peroxidase (APX) and superoxide dismutase (SOD). The output of this study is that strain EPS inoculation mitigates Cd-induced oxidative damage and consequently strain EPS may be beneficial, especially in Cd-contaminated crop fields.\u003c/p\u003e","manuscriptTitle":"The endophyte Stenotrophomonas maltophilia EPS modulates endogenous antioxidant defense in safflower (Carthamus tinctorius L.) under cadmium stress","msid":"","msnumber":"","nonDraftVersions":[{"code":1,"date":"2022-04-13 19:55:43","doi":"10.21203/rs.3.rs-1538673/v1","editorialEvents":[{"type":"communityComments","content":0},{"type":"decision","content":"Major revision","date":"2022-05-03T01:31:43+00:00","index":"","fulltext":""},{"type":"editorInvitedReview","content":"","date":"2022-04-20T02:22:57+00:00","index":"hide","fulltext":""},{"type":"reviewerAgreed","content":"3ac7a98a-c486-459d-96b4-951e13729fa4","date":"2022-04-19T00:57:12+00:00","index":"hide","fulltext":""},{"type":"reviewerAgreed","content":"fcb21269-5054-427f-84c4-7b93e35f2d8b","date":"2022-04-12T08:46:53+00:00","index":"hide","fulltext":""},{"type":"reviewersInvited","content":"","date":"2022-04-12T08:31:59+00:00","index":"","fulltext":""},{"type":"editorAssigned","content":"","date":"2022-04-12T08:23:36+00:00","index":"","fulltext":""},{"type":"checksComplete","content":"","date":"2022-04-09T12:22:52+00:00","index":"","fulltext":""},{"type":"submitted","content":"Archives of Microbiology","date":"2022-04-08T20:45:31+00:00","index":"","fulltext":""}],"status":"published","journal":{"display":true,"email":"[email protected]","identity":"archives-of-microbiology","isNatureJournal":false,"hasQc":true,"allowDirectSubmit":false,"externalIdentity":"aomi","sideBox":"Learn more about [Archives of Microbiology](https://www.springer.com/journal/203)","snPcode":"203","submissionUrl":"https://submission.nature.com/new-submission/203/3","title":"Archives of Microbiology","twitterHandle":"","acdcEnabled":true,"dfaEnabled":true,"editorialSystem":"em","reportingPortfolio":"Springer Hybrid","inReviewEnabled":true,"inReviewRevisionsEnabled":false}}],"origin":"","ownerIdentity":"bc71d15d-d71f-4378-b04d-e5ea3aeaaf75","owner":[],"postedDate":"April 13th, 2022","published":true,"recentEditorialEvents":[],"rejectedJournal":[],"revision":"","amendment":"","status":"under-review","subjectAreas":[],"tags":[],"updatedAt":"2022-06-03T06:44:17+00:00","versionOfRecord":[],"versionCreatedAt":"2022-04-13 19:55:43","video":"","vorDoi":"","vorDoiUrl":"","workflowStages":[]},"version":"v1","identity":"rs-1538673","journalConfig":"researchsquare"},"__N_SSP":true},"page":"/article/[identity]/[[...version]]","query":{"redirect":"/article/rs-1538673","identity":"rs-1538673","version":["v1"]},"buildId":"J0_U0BvcaRcwD8yVFaRlm","isFallback":false,"isExperimentalCompile":false,"dynamicIds":[84888],"gssp":true,"scriptLoader":[]}