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<front>
<journal-meta>
<journal-id journal-id-type="publisher-id">ABC</journal-id>
<journal-id journal-id-type="nlm-ta">Acta Bot Croat</journal-id>
<journal-title-group>
<journal-title>Acta Botanica Croatica</journal-title>
<abbrev-journal-title abbrev-type="pubmed">Acta Bot. Croat.</abbrev-journal-title>
</journal-title-group>
<issn pub-type="ppub">0365-0588</issn>
<issn pub-type="epub">1847-8476</issn>
<publisher><publisher-name>Department of Biology, Faculty of Science, University of Zagreb, Zagreb, Croatia</publisher-name></publisher>
</journal-meta>
<article-meta>
<article-id pub-id-type="publisher-id">ABC-80-191</article-id>
<article-id pub-id-type="doi">10.37427/botcro-2021-022</article-id>
<article-categories><subj-group subj-group-type="heading"><subject>Full articles</subject></subj-group>
</article-categories>
<title-group>
<article-title>Response of <italic>Bacillus cereus</italic> on <italic>Zea mays</italic> under different doses of zinc sulphate</article-title>
</title-group>
<contrib-group>
<contrib contrib-type="author" corresp="yes"><name><surname>Shahzad</surname><given-names>Asim</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref><xref ref-type="aff" rid="aff2"><sup>2</sup></xref><xref ref-type="corresp" rid="cor1"><sup>*</sup></xref></contrib><contrib contrib-type="author"><name><surname>Qin</surname><given-names>Mingzhou</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref></contrib><contrib contrib-type="author"><name><surname>Nazir</surname><given-names>Mudassar</given-names></name><xref ref-type="aff" rid="aff2"><sup>2</sup></xref></contrib><contrib contrib-type="author"><name><surname>Shakoor</surname><given-names>Abdul</given-names></name><xref ref-type="aff" rid="aff3"><sup>3</sup></xref><xref ref-type="aff" rid="aff4"><sup>4</sup></xref></contrib><contrib contrib-type="author"><name><surname>Billah</surname><given-names>Motsim</given-names></name><xref ref-type="aff" rid="aff5"><sup>5</sup></xref></contrib><contrib contrib-type="author"><name><surname>Zaib</surname><given-names>Gul</given-names></name><xref ref-type="aff" rid="aff6"><sup>6</sup></xref></contrib>
<aff id="aff1"><label>1</label><institution>Henan University, The College of Geography and Environment Science, Jinming ave, Kaifeng, China</institution></aff>
    <aff id="aff2"><label>2</label><institution>Mohi-ud-Din Islamic University Nerian Sharif, Department of Botany, Azad Jammu &amp; Kashmir Pakistan</institution></aff>
<aff id="aff3"><label>3</label><institution>Henan University, College of Environment and Planning, Jinming ave, Kaifeng, China</institution></aff>
<aff id="aff4"><label>4</label><institution>Henan University, Laboratory of Geospatial Technology for the Middle and Lower Yellow River Regions, Ministry of Education Kaifeng 475004, Henan, China</institution></aff>
<aff id="aff5"><label>5</label><institution>University of Haripur, Faculty of Applied Sciences, Khyber Pakhtunkhwa, Pakistan</institution></aff>
<aff id="aff6"><label>6</label><institution>Institute of Epigenetics and Epigenomics, Yangzhou University, 48 East Wenhui Road, Yangzhou, Jiangsu, 225009, China</institution></aff>
</contrib-group>
<author-notes>
<corresp id="cor1"><label>*</label>Corresponding author e-mail: <email xlink:href="agron12@yahoo.com">agron12@yahoo.com</email></corresp></author-notes>
<pub-date pub-type="epub-ppub"><month>10</month><year>2021</year></pub-date>
<volume>80</volume>
<issue>2</issue>
<fpage>191</fpage>
<lpage>198</lpage>
<abstract>
<p>Anthropogenic activities have added a large amount of heavy metals to the environment. Heavy metal contaminants affect the physiological and biological properties of soil and plant health. Zinc (Zn) is an essential micronutrient and it promotes plant growth and development but a higher concentration of the metal causes reduction in plant growth. The present study was aimed to evaluate the response of <italic>Bacillus cereus</italic> on maize plants at different concentrations of ZnSO<sub>4</sub> (20, 40 and 60 mg kg<sup>-1</sup>) amended in the soil under pot experiment conditions. The experiment was conducted by using complete randomized design (CRD) with three replications. Higher doses of ZnSO<sub>4</sub> inhibited maize growth and nutrient uptake. However, inoculation of maize seeds with <italic>Bacillus cereus</italic> at 20 mg kg<sup>-1</sup> concentration of ZnSO<sub>4</sub> increased seed germination about 39% and plant height by 15%. Moreover, 17% increase in leaf length and a 7% increase in leaf number were observed as compared to control at 20 mg kg<sup>-1</sup> concentrations of ZnSO<sub>4</sub>. Reductions in all growth parameters were observed with 60 mg kg<sup>-1</sup> concentration of ZnSO<sub>4</sub>. The Zn uptake was 75% higher in treatment T8 (uninoculated seeds with 60 mg kg<sup>-1</sup> concentration of ZnSO<sub>4</sub>) as compared to treatments which were inoculated and grown under different zinc concentrations. The results suggest that <italic>Bacillus cereus</italic> has good potential to remediate Zn from soil as well as to reduce the phyto-availibility and phytotoxicity of zinc.</p>
</abstract>
<kwd-group kwd-group-type="author"><title>Keywords: </title><kwd>maize</kwd><kwd>nutrient availability</kwd><kwd>phytoextraction</kwd><kwd>phytotoxicity</kwd><kwd>plant microbial interaction</kwd><kwd>zinc</kwd></kwd-group>
</article-meta>
</front>
<body>
<sec sec-type="intro">
<title>Introduction</title>
<p>Soil is a mixture of different components, organic matter (5%), minerals (45%), gases (25%), and liquids (25%). Besides this, several organisms which support and maintain life on Earth are also found in the soil. Soil provides several ecosystem services by maintaining biogeochemical cycles and protection against erosion (<xref ref-type="bibr" rid="r32">Tahat et al. 2020</xref>). Healthy soil acts as a dynamic living system that delivers multiple ecosystem services, such as plant productivity, sustaining water quality and controlling soil nutrient recycling decomposition. Soil health is closely associated with sustainable agriculture, because soil microorganism diversity and activity are the main components of the soil health (<xref ref-type="bibr" rid="r32">Tahat et al. 2020</xref>). Anthropogenic and industrial activities, facilities and products such as mining of natural resources, electroplating, smelting, fertilizers, pesticides, tanneries add a large number of contaminants to our natural environment. These contaminants affect the physiological and biological properties of soil (<xref ref-type="bibr" rid="r2">Arivalagan et al. 2014</xref>). Among different contaminants, heavy metals such arsenic (As), cadmium (Cd), lead (Pb), copper (Cu), chromium (Cr), nickel (Ni), zinc (Zn), aluminum (Al) and manganese (Mn) are the most common (<xref ref-type="bibr" rid="r39">Ullah et al. 2015</xref>). Heavy metals have shown negative impacts on soil fertility and soil microbial community (<xref ref-type="bibr" rid="r5">Chu 2018</xref>). They are not soluble in water and are not readily degradable; therefore, they remain insoluble in the soil. Later on, they are assimilated by plant roots. In this way, heavy metals are transferred to different trophic levels of the ecosystem and contaminate the food chain (<xref ref-type="bibr" rid="r34">Tchounwou et al. 2012</xref>).</p>
<p>Zinc is an essential micronutrient which promotes plant growth and development (<xref ref-type="bibr" rid="r16">Hefferon 2019</xref>); however, higher concentration of Zn causes root blunt, cell wall thickening, reduction in cell division, cell elongation, and disruption in cell organelles and an increase in the number of the nucleoli (<xref ref-type="bibr" rid="r13">Gli&#x0144;ska et al. 2016</xref>, <xref ref-type="bibr" rid="r31">Taghizadeh et al. 2018</xref>). Plants have different defense mechanisms or strategies for tolerance or detoxification, whenever they are exposed to heavy metal stress condition. In addition, microorganisms from soil assist plants to degrade a huge variety of contaminants. In contaminated soil, microorganisms can modify and adopt various mechanisms that convert toxic substances into a less toxic form (<xref ref-type="bibr" rid="r19">Jaiswal et al. 2017</xref>). These mechanisms include biosorption, bioaccumulation, biotransformation, and bio-mineralization. <italic>Pseudomonas</italic>, <italic>Alcaligenes</italic>, <italic>Sphingomonas</italic>, <italic>Rhodococcus</italic> and <italic>Mycobacterium</italic> have the potential to detoxify contaminants in nature (<xref ref-type="bibr" rid="r40">Vergani et al. 2017</xref>). Some bacterial species such as <italic>Bacillus</italic> and <italic>Pseudomonas</italic> are generally used for the remediation of heavy metals from contaminated water and soil, as these bacterial strains have more metal binding affinities (<xref ref-type="bibr" rid="r2">Arivalagan et al. 2014</xref>, <xref ref-type="bibr" rid="r39">Ullah et al. 2015</xref>). Plant growth-promoting bacteria increase plant growth and development by increasing accessibility of nutrients (<xref ref-type="bibr" rid="r4">Bulgarelli et al. 2013</xref>), which contributes to plant health and increases their biomass and absorbing capacity to overcome stress (<xref ref-type="bibr" rid="r42">Weyens et al. 2013</xref>). <italic>Rhizobia</italic> have the potential to remove organic and metal contamination by degrading organic contaminants (<xref ref-type="bibr" rid="r35">Teng et al. 2015</xref>). Besides, bacteria have the ability to produce phytohormones such as auxins, cytokinins and gibberellins, which control all aspects of plant growth and development (<xref ref-type="bibr" rid="r12">Glick 2010</xref>). Plant growth-promoting bacteria enhance plant growth in stress conditions through various mechanisms including nitrogen (N) and phosphorus (P) solubilization, siderophore production and 1-aminocyclopropane-1-carboxylic acid (ACC) deaminase production (<xref ref-type="bibr" rid="r9">Fatima et al. 2017</xref>).</p>
<p>Increased concentration of heavy metals inhibits normal plant functioning by disturbing protein structure; this alteration hampers metabolic processes (<xref ref-type="bibr" rid="r14">Hall 2002</xref>). The change in in protein structure can cause mutation in various physiological processes in plants such as photosynthesis, respiration, and enzymatic activities (<xref ref-type="bibr" rid="r17">Hossain et al. 2012</xref>). Plants have different defense mechanisms or strategies for tolerance or detoxification whenever they are exposed to elevated concentration of heavy metals. The first step in metal tolerance is inhibition or restriction of heavy metal entry into plant root (<xref ref-type="bibr" rid="r41">Viehweger 2014</xref>). Failure of the first step activates the mechanism of phytosequestration which permits heavy metals to enter in intracellular compartments (<xref ref-type="bibr" rid="r24">Patra et al. 2004</xref>), which produce different substances like phytochelatins (PCs), organic acid, polysaccharides and metallothionein (MTs), which are the two best-characterized metal-binding ligands in plant cells that help a plant to detoxify heavy metals (<xref ref-type="bibr" rid="r6">Dalvi and Bhalerao 2013</xref>). If all these strategies fail, plants activate their antioxidant defense mechanism which can help the plant by inducing reactive oxygen species (ROS), which inhibit most cellular processes at various levels of metabolism. ROS, being highly unstable, could play dual role (1) damaging cellular components and (2) act as an important secondary messenger for inducing plant defense system. Cells are equipped with enzymatic and non-enzymatic defense mechanisms to counteract this. (<xref ref-type="bibr" rid="r30">Sytar et al. 2013</xref>, <xref ref-type="bibr" rid="r23">Manara 2012</xref>).</p>
<p>Any plant used for phytoremediation should not be metal-tolerant, and must be fast growing with the potential to produce high biomass. Maize is mainly used in phytoextraction due to the fact that it is a common and rapidly growing crop, which possesses an extensive fibrous root system and can tolerate stress conditions (<xref ref-type="bibr" rid="r8">Farooq et al. 2015</xref>). Therefore, maize plants are suitable for the extraction of heavy metals from contaminated soil (<xref ref-type="bibr" rid="r22">Lu et al. 2015</xref>). There is insufficient information about the fate of bacterial inoculation in maize edible and non-edible parts to enhance maize tolerance in heavy metal soils (<xref ref-type="bibr" rid="r28">Shahzad et al. 2016</xref>). Henceforth, present investigation is aimed to evaluate the role of <italic>Bacillus cereus</italic> strain in enhancing the phytoextraction ability of maize plant under Zn contaminated soil conditions.</p>
</sec>
<sec sec-type="materials|methods">
<title>Materials and methods</title>
<sec>
<title>Bacterial strain</title>
<p><italic>Bacillus cereus</italic> (Accession no. KR232400) was selected on the basis of its plant growth promoting potential (<xref ref-type="bibr" rid="r27">Shahzad et al. 2020</xref>). The strain was obtained from phyto-hormone laboratory at Quaid-i-Azam University, Pakistan. Bacterial strain was previously identified by 16S rRNA gene sequencing (<xref ref-type="bibr" rid="r28">Shahzad et al. 2016</xref>).</p>
</sec>
<sec>
<title>Preparation of heavy metal solution</title>
<p>Three different concentrations of Zn solution (20, 40 and 60 mg kg<sup>-1</sup>) for maize plant treatments were prepared in pure distilled water by dissolving zinc sulfate (ZnSO<sub>4</sub>). We selected these three concentrations on the basis of previous scientific data (<xref ref-type="bibr" rid="r21">Long et al. 2003</xref>, <xref ref-type="bibr" rid="r43">Yang et al. 2005</xref>). Pure distilled water was used as the control for the experiment. 200 mL of each solution was added in 1 kg of potted soil.</p>
</sec>
<sec>
<title>Preparation of inoculum</title>
<p>For the preparation of inoculum, five ml of nutrient broth medium (Oxoid, UK) was autoclaved in test tubes for cultivation of bacterial strain. Bacteria were incubated in a shaker incubator (EXCELLA E24 Germany) at 37 &#x00BA;C and 150 rpm for 48-72 h. Thereafter, the culture was centrifuged at 3000 rpm for 10 min. The pellet was re-suspended in autoclaved distilled water and the optical density (OD) was adjusted to 0.100 at 660 nm with UV-VIS spectrophotometer (UV-VIS Double Beam Spectrophotometer, Model NO: AE-S90-2D A &amp; E Lab (UK) Co., Ltd.). Bacterial density was 10<sup>6</sup> cells mL<sup>-1</sup> at optical density of 0.10 at 660 nm. The optical density was adjusted by adding about 200 ml sterile water to pure bacterial pellets.</p>
</sec>
<sec>
<title>Preparation of treatment applications and seed inoculation</title>
<p>Kashmir Gold variety maize (<italic>Zea mays</italic> L) seeds were collected from the National Agricultural Research Centre, Islamabad, Pakistan. The seeds were surface sterilized by washing with 95% ethanol, following by soaking in 10% Clorox for 2-3 minutes. The seeds were washed successively 2-3 times in autoclaved distilled water.</p>
<p>For experiment preparation, seeds were soaked in the <italic>B. cereus</italic> inoculum for 2-3 hrs, after that about 10 seeds were sown in each pot. Different concentrations of Zn solutions (100, 200 and 300 mg L<sup>-1</sup>) and distilled water was added to each pot. Eight different treatments with three replicates were made. Detailed explanation of treatments is given in <xref ref-type="table" rid="t1">Table 1</xref></p>
<table-wrap id="t1" position="float">
<label>Tab. 1</label><caption><title>Kashmir Gold variety <italic>Zea mays</italic> seeds were inoculated (+) or not (-) with <italic>Bacillus cereus</italic>, germinated and grown in soil supplemented with 20, 40 or 60 mg kg<sup>-1</sup> ZnSO4. Eight treatments (T) were applied.</title>
</caption>
<table frame="hsides" rules="groups">
<col width="32.87%"/>
<col width="39.68%"/>
<col width="27.45%"/>
<thead>
<tr>
<th valign="top" align="center" scope="col" style="border-top: solid 0.50pt; border-bottom: solid 0.50pt"><bold>Treatments</bold></th>
<th valign="top" align="center" scope="col" style="border-top: solid 0.50pt; border-bottom: solid 0.50pt"><bold><italic>Bacillus cereus</italic> inoculation</bold></th>
<th valign="top" align="center" scope="col" style="border-top: solid 0.50pt; border-bottom: solid 0.50pt"><bold>ZnSO4 (mg kg<sup>-1</sup>)</bold></th>
</tr>
</thead>
<tbody>
<tr>
<td valign="top" align="center" style="border-top: solid 0.50pt" scope="row">T1</td>
<td valign="top" align="center" style="border-top: solid 0.50pt">-</td>
<td valign="top" align="center" style="border-top: solid 0.50pt">0</td>
</tr>
<tr>
<td valign="top" align="center" scope="row">T2</td>
<td valign="top" align="center">+</td>
<td valign="top" align="center">0</td>
</tr>
<tr>
<td valign="top" align="center" scope="row">T3</td>
<td valign="top" align="center">+</td>
<td valign="top" align="center">20</td>
</tr>
<tr>
<td valign="top" align="center" scope="row">T4</td>
<td valign="top" align="center">+</td>
<td valign="top" align="center">40</td>
</tr>
<tr>
<td valign="top" align="center" scope="row">T5</td>
<td valign="top" align="center">+</td>
<td valign="top" align="center">60</td>
</tr>
<tr>
<td valign="top" align="center" scope="row">T6</td>
<td valign="top" align="center">-</td>
<td valign="top" align="center">20</td>
</tr>
<tr>
<td valign="top" align="center" scope="row">T7</td>
<td valign="top" align="center">-</td>
<td valign="top" align="center">40</td>
</tr>
<tr>
<td valign="top" align="center" style="border-bottom: solid 0.50pt" scope="row">T8</td>
<td valign="top" align="center" style="border-bottom: solid 0.50pt">-</td>
<td valign="top" align="center" style="border-bottom: solid 0.50pt">60</td>
</tr>
</tbody></table></table-wrap>
</sec>
<sec>
<title>Parameter measured:</title>
<p>The percentage germination was noted after seven day of sowing. Maize seedlings were uprooted after 21 days of sowing, after which root length (cm), plant height (cm), leaf length (cm), number of leaves and fresh plant weight parameters were recorded. Each treatment contained three replicates and 5 plants from each replicate were measured.</p>
</sec>
<sec>
<title>Soil nutrient analyses</title>
<p>Determination of macro- and micro-nutrients (Na, Ca, Mg, K, P, N, Fe, Cu, Cr, Co, Zn, and Mn) was carried out by following the ammonium bicarbonate and diethylenetriamine pentaacetic acid (DTPA) method as described by <xref ref-type="bibr" rid="r29">Soltanpour and Schwab (1977)</xref>. The 0.005 M ammonium bicarbonate and (DTPA) solution was prepared by adding 1.97 g of DTPA to 800 mL of distilled water. About 2 mL of ammonium hydroxide (NH<sub>4</sub>OH) was added to facilitate dilution and to prevent effervescence due to ammonium bicarbonate addition. When DTPA was dissolved completely, 79.06 g of ammonium bicarbonate (NH<sub>4</sub>HCO<sub>3</sub>) was added. The pH of the solution was adjusted to 7.6 by adding 2 mL of ammonium hydroxide. Final volume was adjusted to 1 L with the addition of distilled water. For the analysis of different nutrient, 10 g of soil sample was mixed with 15 mL of distilled water. The suspension was stirred for 30 minutes on a magnetic stirrer. After stirring step, suspension was filtered. Two mL of filtrate was removed and 18 mL of distilled water was added for nutrient analysis.</p>
</sec>
<sec>
<title>Plant nutrient analysis</title>
<p>The perchloric-acid digestion scheme was used to determine the content of various nutrients in maize plants (<xref ref-type="bibr" rid="r1">Allen et al. 1974</xref>). A solution of nitric acid, sulfuric acid, and perchloric acid in the ratio 5:1:0.1 (6.5 mL) was added to 0.25 g of plant material in a 50 mL flask and the mixture was heated on the hot plate in the fume hood to complete the digestion process. The formation of white fumes in the mixture confirmed the completion of digestion of the plant extract. Thereafter, distilled water (few drops) was poured into the flask and the mixture was allowed to cool. The digested plant extract samples were transferred to the volumetric flasks (50 mL) and the volume was raised up to 50 mL by the addition of distilled water. The samples were filtered with Whatman no.42 filter paper and were stored for further element analysis. The concentration of different elements/nutrients present in the plant samples were measured by atomic absorption spectrophotometer (Shimadzu AA-670 Germany).</p>
</sec>
<sec>
<title>Statistical analysis</title>
<p>The experiment was conducted in a completely randomized design (CRD) by using Statistic 8.1.1. (<ext-link ext-link-type="uri" xlink:href="https://statistix.informer.com/8.1/">https://statistix.informer.com/8.1/</ext-link>). The results are the compare means and standard error of means of three replicates of a treatment. Five plants from each replicate were measured.</p>
</sec>
</sec>
<sec sec-type="results">
<title>Results</title>
<sec>
<title>Effects on seed germination</title>
<p>Percentage germination of maize seeds has shown variations among inoculated and uninoculated seeds (<xref ref-type="fig" rid="f1">Fig. 1a</xref>). Maximum seed germination (%) was observed in <italic>B. cereus-</italic>inoculated seeds in combination with 20 mg kg<sup>-1</sup> ZnSO<sub>4</sub> (treatment T3), which was significantly higher than control (39%) and the majority of the treatments. High germination percentage was also recorded in <italic>B. cereus-</italic>inoculated seeds in combination with 40 mg kg<sup>-1</sup> ZnSO<sub>4</sub> (treatment T4), which was significantly higher than the treatment of uninoculated seeds with 60 mg kg<sup>-1</sup> ZnSO<sub>4</sub> (treatment T8), where the lowest values were obtained (germination reduction of 9% as compared to control).</p>
<fig id="f1" position="float" fig-type="figure"><label>Fig. 1</label><caption><p>Effect of zinc on Kashmir Gold variety <italic>Zea mays</italic> seed germination % (a), root length (b), leaf length (c) and number of leaves (d). Plants were measured at 21 day after sowing. Results, expressed as means &#x00B1; standard error (SE) of 3 replicates and each replica contains 10 plants. Results were compared by using compare means with completely randomized design (CRD). Treatments sharing a common letter (a&gt;b&gt;c) are similar, otherwise differ significantly at P &lt; 0.05. T1 &#x2013; control, T2 &#x2013; <italic>Bacillus cereus-</italic>inoculated seeds, T3 &#x2013; <italic>B. cereus-</italic>inoculated seed + 20 mg kg<sup>-1</sup> ZnSO<sub>4</sub>, T4 &#x2013; <italic>B. cereus-</italic>inoculated seeds + 40 mg kg<sup>-1</sup> ZnSO<sub>4</sub>, T5 &#x2013; <italic>B. cereus-</italic>inoculated seeds + 60 mg kg<sup>-1</sup> ZnSO<sub>4</sub>, T6 &#x2013; uninoculated seeds + 20 mg kg<sup>-1</sup> Zn SO<sub>4</sub>, T7 &#x2013; uninoculated seeds + 40 mg kg<sup>-1</sup> ZnSO<sub>4</sub>, T8 &#x2013; uninoculated seeds + 60 mg kg<sup>-1</sup> ZnSO<sub>4</sub>.</p></caption><graphic xlink:href="ABC-80-191-f1"></graphic></fig>
</sec>
<sec>
<title>Effects on root length, leaf length and number of leaves</title>
<p>The root length was only mildly affected by investigated treatments (<xref ref-type="fig" rid="f1">Fig. 1b</xref>). The maximum increase in the root length (15%) was observed in <italic>B. cereus</italic> inoculated seeds in combination with 20 mg kg<sup>-1</sup> ZnSO<sub>4</sub> (treatment T3), although it was not significant compared to control. Similar increase in root length (14%) was also recorded for <italic>B. cereus-</italic>inoculated seed (treatment T2 treatments). On the contrary, the 19% reduction in root length was observed in the treatment of uninoculated seeds exposed to60 mg kg<sup>-1</sup> ZnSO<sub>4</sub> (treatment T8), which was not significant compared to control, but was significantly reduced in comparison to treatments T2 and T3. Other treatments exhibited values similar to those of control</p>
<p>Maximum increase in leaf length (17%) was observed in <italic>B. cereus-</italic>inoculated seeds in combination with 20 mg kg<sup>-1</sup> ZnSO<sub>4</sub> (treatment T3), although it was not significant as compared to control and other treatments of inoculated seeds; however, it was significantly higher in comparison to result obtained for uninoculated seeds (<xref ref-type="fig" rid="f1">Fig. 1c</xref>). Namely, all treatments of uninoculated seeds resulted in reduction in leaf length, which was particularly after exposure to 20 mg kg<sup>-1</sup> ZnSO<sub>4</sub> (treatment T6).</p>
<p>Maximum number of leaves (1% increase compared to control) was observed in <italic>B. cereus-</italic>inoculated seeds in combination with 40 mg kg<sup>-1</sup> ZnSO<sub>4</sub> (treatment T4), although this value was not significantly different as compared to the majority of the treatments; the only exception was the treatment of uninoculated seeds exposed to 20 mg kg<sup>-1</sup> ZnSO<sub>4</sub> (treatment T6), which exhibited the lowest value (7% decrease compared to control) (<xref ref-type="fig" rid="f1">Fig. 1d</xref>).</p>
</sec>
<sec>
<title>Effects on plant height, fresh weight and zinc uptake</title>
<p>The inoculation of maize seeds with <italic>B. cereus</italic> significantly increased the fresh weight and height of maize plants (<xref ref-type="fig" rid="f2">Fig. 2</xref>). A significantly higher increase in fresh weight was observed upon exposure of inoculated seeds to 20 mg kg<sup>-1</sup> ZnSO<sub>4</sub> (treatment T3, 80% increase) and 40 mg kg<sup>-1</sup> ZnSO<sub>4</sub> (treatment T4, 62% increased) in comparison to control and the treatments of uninoculated seeds. On the contrary, a significant reduction in plant fresh weight as compared to control was observed in all treatments of uninoculated seeds, with the maximum reduction of 27% recorded upon exposure to 60 mg kg<sup>-1</sup> ZnSO<sub>4</sub> (treatment T8) (<xref ref-type="fig" rid="f2">Fig. 2b</xref>).</p>
<fig id="f2" position="float" fig-type="figure"><label>Fig. 2</label><caption><p>Effect of zinc on Kashmir Gold variety <italic>Zea mays</italic> plant height (a), plant fresh weight (b) zinc uptake (c). Plants were measured at 21 day after sowing. Results, expressed as means &#x00B1; standard error (SE) of 3 replicates and each replica contains 10 plants. Results were compared by using compare means with completely randomized design (CRD). Different letters (a&gt; b&gt; c) indicate treatments sharing a common letter are similar but otherwise differ significantly at P &lt; 0.05. T1 &#x2013; control, T2 &#x2013; <italic>B. cereus-</italic>inoculated seeds, T3 &#x2013; <italic>B. cereus-</italic>inoculated seed + 20 mg kg<sup>-1</sup> ZnSO<sub>4</sub>, T4 &#x2013; <italic>B. cereus-</italic>inoculated seeds + 40 mg kg<sup>-1</sup> ZnSO<sub>4</sub>, T5 &#x2013; <italic>B. cereus-</italic>inoculated seeds + 60 mg kg<sup>-1</sup> ZnSO<sub>4</sub>, T6 &#x2013; uninoculated seeds + 20 mg kg<sup>-1</sup> Zn, T7 &#x2013; uninoculated seeds + 40 mg kg<sup>-1</sup> ZnSO<sub>4</sub>, T8 &#x2013; uninoculated seeds + 60 mg kg<sup>-1</sup> ZnSO<sub>4</sub>.</p></caption><graphic xlink:href="ABC-80-191-f2"></graphic></fig>
<p>Exposure of inoculated seeds to ZnSO<sub>4</sub> slightly improved the plant height (treatments T3, T4 and T5) as compared to control; the maximum value (12% increase as compared to control) was obtained upon exposure to 20 mg kg<sup>-1</sup> Zn (treatment T3). On the other hand, exposure of uninoculated seeds to the same Zn concertation (20 mg kg<sup>-1</sup>) resulted in a reduction in plant height up to 19% (<xref ref-type="fig" rid="f2">Fig. 2a</xref>).</p>
<p>Zinc uptake was reduced in the majority of the treatments with inoculated seeds as compared to control; significantly for treatments T2 and T3 (exposure to 100 mg L<sup>-1</sup> ZnSO<sub>4</sub>), and notably for treatment T4 (exposure to 49 mg kg<sup>-1</sup>); reduced Zn uptake was 49%, 44% and 22% in T2, T3 and T4 respectively (<xref ref-type="fig" rid="f2">Fig. 2c</xref>). However, the exposure of inoculated seeds to the highest tested Zn concentration (treatment T5) resulted in a significantly higher Zn uptake as compared to control. Among treatments with uninoculated seeds, exposure to 20 mg kg<sup>-1</sup> (treatment T6) resulted in a value similar to that of control, while upon treatment with 40 and 60 mg kg<sup>-1</sup> Zn (treatments T7 and T8, respectively) Zn uptake was significantly higher; the maximum increase (75% as compared to control) was observed in treatment T8 (<xref ref-type="fig" rid="f2">Fig. 2c</xref>).</p>
</sec>
<sec>
<title>Nutrients status of soil and accumulation of nutrients by maize plant</title>
<p>Different nutrients including Ca, Mg, K, Na, Fe, Cd, Cu, Cr, Zn, Co and Ni were detected in soil samples (<xref ref-type="table" rid="t2">Tab. 2</xref>). The plant nutrient status (<xref ref-type="table" rid="t3">Tab. 3</xref>) showed that the Cu content decreased in majority of the treatments as compared to control; the only exceptions were treatments T3 and T8. The Mn content was significantly elevated in the treatment of plants from inoculated seeds exposed to 20 mg kg<sup>-1</sup> ZnSO<sub>4</sub> (treatment T3), while the exposure of plants from uninoculated seeds to 40 mg kg<sup>-1</sup> ZnSO<sub>4</sub> (treatment T7) resulted in significantly lower Mn content as compared to control. Reduced Ni and Co contents were recorded in the majority of treatments as compared to control. Seed inoculation with <italic>B. cereus</italic> in general decreased the Na content as compared to values obtained in uninoculated plants, since the higher values were obtained in treatments of plants from uninoculated seeds (treatments T6, T7 and T8) as compared to treatments of plants from inoculated seeds to the corresponding Zn concentrations. Seed inoculation with <italic>B. cereus</italic> increased Cr content in plants as compared to control as well as to the treatments of plants from uninoculated seeds upon exposure to 20 and 40 mg kg<sup>-1</sup> ZnSO<sub>4</sub> (treatments T3 and T4) as compared to treatments T6 and T7, respectively). Fe content was significantly elevated in plants from inoculated seeds upon exposure to 40 and 60 mg kg<sup>-1</sup> ZnSO<sub>4</sub> compared to control as well as to the exposure of plants from uninoculated seeds to the same Zn concentration. Seed inoculation with <italic>B. cereus</italic> in general increased the Ca and Mg uptake in all investigated treatments as compared to control, with higher values obtained in plants from inoculated seeds compared to the uninoculated ones. K content was significantly higher in plants from inoculated seeds as compared to the control as well as to plants from uninoculated seeds exposed to the corresponding Zn concentrations.</p>
<table-wrap id="t2" position="float">
<label>Tab. 2</label><caption><title>Analysis of soil micro and macro nutrients before addition of ZnSO<sub>4</sub> and sowing of <italic>Zea mays</italic> measured in mg kg<sup>-1</sup>. Results are expressed as means &#x00B1; standard error (SE) of three soil samples.</title>
</caption>
<table frame="hsides" rules="groups">
<col width="57.92%"/>
<col width="42.08%"/>
<thead>
<tr>
<th valign="top" align="center" scope="col" style="border-top: solid 0.50pt; border-bottom: solid 0.50pt"><bold>Nutrient </bold></th>
<th valign="top" align="center" scope="col" style="border-top: solid 0.50pt; border-bottom: solid 0.50pt"><bold>Soil (mg kg<sup>-1</sup>)</bold></th>
</tr>
</thead>
<tbody>
<tr>
<td valign="top" align="center" style="border-top: solid 0.50pt" scope="row">Ca</td>
<td valign="top" align="right" style="border-top: solid 0.50pt">19.6 &#x00B1; 1.11</td>
</tr>
<tr>
<td valign="top" align="center" scope="row">Mg</td>
<td valign="top" align="right">2.46 &#x00B1; 0.23</td>
</tr>
<tr>
<td valign="top" align="center" scope="row">K</td>
<td valign="top" align="right">1.67 &#x00B1; 0.21</td>
</tr>
<tr>
<td valign="top" align="center" scope="row">Na</td>
<td valign="top" align="right">22.39 &#x00B1; 0.66</td>
</tr>
<tr>
<td valign="top" align="center" scope="row">Fe</td>
<td valign="top" align="right">3.18 &#x00B1; 0.12</td>
</tr>
<tr>
<td valign="top" align="center" scope="row">Cd</td>
<td valign="top" align="right">4.39 &#x00B1; 0.19</td>
</tr>
<tr>
<td valign="top" align="center" scope="row">Cu</td>
<td valign="top" align="right">11.20 &#x00B1; 0.44</td>
</tr>
<tr>
<td valign="top" align="center" scope="row">Cr</td>
<td valign="top" align="right">10.5 &#x00B1; 0.12</td>
</tr>
<tr>
<td valign="top" align="center" scope="row">Zn</td>
<td valign="top" align="right">8.9 &#x00B1; 0.11</td>
</tr>
<tr>
<td valign="top" align="center" scope="row">Co</td>
<td valign="top" align="right">0.19 &#x00B1; 0.02</td>
</tr>
<tr>
<td valign="top" align="center" scope="row">Ni</td>
<td valign="top" align="right">2.23 &#x00B1; 0.15</td>
</tr>
<tr>
<td valign="top" align="center" style="border-bottom: solid 0.50pt" scope="row">Mn</td>
<td valign="top" align="right" style="border-bottom: solid 0.50pt">6.22 &#x00B1; 0.27</td>
</tr>
</tbody></table></table-wrap>
<table-wrap id="t3" position="float">
<label>Tab. 3</label><caption><title>Accumulation of micro and macro nutrients by Kashmir Gold variety <italic>Zea mays</italic> plants. Plants were measured at 21 day after sowing. Results, expressed as means &#x00B1; standard error (SE) of three replicates and each replica contains 5 plants. Results were compared by using compare means with completely randomized design (CRD). Treatments sharing a common letter (A&gt;B&gt;C) are similar, otherwise differ significantly at P &lt;0.05. T1 &#x2013; control, T2 &#x2013; <italic>Bacillus cereus-</italic>inoculated seeds, T3 &#x2013; <italic>B. cereus-</italic>inoculated seed + 20 mg kg<sup>-1</sup> ZnSO<sub>4</sub>, T4 &#x2013; <italic>B. cereus-</italic>inoculated seeds + 40 mg kg<sup>-1</sup> ZnSO<sub>4</sub>, T5 &#x2013; <italic>B. cereus-</italic>inoculated seeds + 60 mg kg<sup>-1</sup> ZnSO<sub>4</sub>, T6 &#x2013; uninoculated seeds + 20 mg kg<sup>-1</sup> Zn, T7 &#x2013; uninoculated seeds + 40 mg kg<sup>-1</sup> ZnSO<sub>4</sub>, T8 &#x2013; uninoculated seeds + 60 mg kg<sup>-1</sup> ZnSO<sub>4</sub>.</title>
</caption>
<table frame="hsides" rules="groups">
<col width="7.46%"/>
<col width="10.67%"/>
<col width="11.56%"/>
<col width="10.59%"/>
<col width="11.56%"/>
<col width="11.56%"/>
<col width="12.52%"/>
<col width="11.56%"/>
<col width="12.52%"/>
<thead>
<tr>
<th rowspan="2" valign="top" align="left" scope="col" style="border-top: solid 0.50pt; border-bottom: solid 0.50pt">Nutrient</th>
<th colspan="8" valign="top" align="center" scope="colgroup" style="border-top: solid 0.50pt; border-bottom: solid 0.50pt">Nutrient concentration (mg kg<sup>-1</sup>)</th>
</tr>
</thead>
<tbody>
<tr>
<td valign="top" colspan="1" align="center" style="border-top: solid 0.50pt; border-bottom: solid 0.50pt" scope="row">T1</td>
<td valign="top" align="center" style="border-top: solid 0.50pt; border-bottom: solid 0.50pt">T2</td>
<td valign="top" align="center" style="border-top: solid 0.50pt; border-bottom: solid 0.50pt">T3</td>
<td valign="top" align="center" style="border-top: solid 0.50pt; border-bottom: solid 0.50pt">T4</td>
<td valign="top" align="center" style="border-top: solid 0.50pt; border-bottom: solid 0.50pt">T5</td>
<td valign="top" align="center" style="border-top: solid 0.50pt; border-bottom: solid 0.50pt">T6</td>
<td valign="top" align="center" style="border-top: solid 0.50pt; border-bottom: solid 0.50pt">T7</td>
<td valign="top" align="center" style="border-top: solid 0.50pt; border-bottom: solid 0.50pt">T8</td>
</tr>
<tr>
<td valign="top" align="justify" style="border-top: solid 0.50pt" scope="row">Cu</td>
<td valign="top" align="justify" style="border-top: solid 0.50pt">0.33 &#x00B1; 0.01 AB</td>
<td valign="top" align="justify" style="border-top: solid 0.50pt">0.15 &#x00B1; 0.001 D</td>
<td valign="top" align="justify" style="border-top: solid 0.50pt">0.38 &#x00B1; 0.02 A</td>
<td valign="top" align="justify" style="border-top: solid 0.50pt">0.20 &#x00B1; 0.001 D</td>
<td valign="top" align="justify" style="border-top: solid 0.50pt">0.30 &#x00B1; 0.02 BC</td>
<td valign="top" align="justify" style="border-top: solid 0.50pt">0.21 &#x00B1; 0.02 CD</td>
<td valign="top" align="justify" style="border-top: solid 0.50pt">0.16 &#x00B1; 0.02D</td>
<td valign="top" align="justify" style="border-top: solid 0.50pt">0.2&#x00B1;0.01 D</td>
</tr>
<tr>
<td valign="top" align="justify" scope="row">Mn</td>
<td valign="top" align="justify">0.12 &#x00B1; 0.01 BC</td>
<td valign="top" align="justify">0.14 &#x00B1; 0.01 B</td>
<td valign="top" align="justify">0.2 &#x00B1; 0.02 A</td>
<td valign="top" align="justify">0.07 &#x00B1; 0.003 CD</td>
<td valign="top" align="justify">0.09 &#x00B1; 0.01 BCD</td>
<td valign="top" align="justify">0.06 &#x00B1; 0.01 CD</td>
<td valign="top" align="justify">0.05 &#x00B1; 0.01D</td>
<td valign="top" align="justify">0.09&#x00B1; 0.01 CD</td>
</tr>
<tr>
<td valign="top" align="justify" scope="row">Ni</td>
<td valign="top" align="justify">0.02 &#x00B1; 0.001 B</td>
<td valign="top" align="justify">0.008 &#x00B1; 0.0002 D</td>
<td valign="top" align="justify">0.03 &#x00B1; 0.002 A</td>
<td valign="top" align="justify">0.013 &#x00B1; 3.33 BC</td>
<td valign="top" align="justify">0.007 &#x00B1; 0.001 D</td>
<td valign="top" align="justify">0.007 &#x00B1; 0.0004 D</td>
<td valign="top" align="justify">0.009 &#x00B1;0.002CD</td>
<td valign="top" align="justify">0.009 &#x00B1; 0.0003 CD</td>
</tr>
<tr>
<td valign="top" align="justify" scope="row">Co</td>
<td valign="top" align="justify">0.10 &#x00B1; 0.001 B</td>
<td valign="top" align="justify">0.11 &#x00B1; 0.002 A</td>
<td valign="top" align="justify">0.03 &#x00B1; 0.001 F</td>
<td valign="top" align="justify">0.05 &#x00B1; 0.002 DE</td>
<td valign="top" align="justify">0.03 &#x00B1; 0.0001 F</td>
<td valign="top" align="justify">0.04 &#x00B1; 3.85 EF</td>
<td valign="top" align="justify">0.05 &#x00B1; 0.005CD</td>
<td valign="top" align="justify">0.06 &#x00B1; 0.001 C</td>
</tr>
<tr>
<td valign="top" align="justify" scope="row">Na</td>
<td valign="top" align="justify">11.3 &#x00B1; 0.34 E</td>
<td valign="top" align="justify">16.1 &#x00B1; 0.7CD E</td>
<td valign="top" align="justify">13.3 &#x00B1; 1.0 DE</td>
<td valign="top" align="justify">29.19 &#x00B1; 0.5 AB</td>
<td valign="top" align="justify">33.8 &#x00B1; 0.52 A</td>
<td valign="top" align="justify">35.9 &#x00B1; 0.9 A</td>
<td valign="top" align="justify">23.6 &#x00B1; 3.6BC</td>
<td valign="top" align="justify">19.1 &#x00B1; 0.2 CD</td>
</tr>
<tr>
<td valign="top" align="justify" scope="row">Cr</td>
<td valign="top" align="justify">0.20 &#x00B1; 0.01 BC</td>
<td valign="top" align="justify">0.3 &#x00B1; 0.02 AB</td>
<td valign="top" align="justify">0.4 &#x00B1; 0.02 A</td>
<td valign="top" align="justify">0.32 &#x00B1; 0.05 A</td>
<td valign="top" align="justify">0.20 &#x00B1; 0.014 BC</td>
<td valign="top" align="justify">0.12 &#x00B1; 0.003 C</td>
<td valign="top" align="justify">0.13 &#x00B1; 0.02C</td>
<td valign="top" align="justify">0.1 &#x00B1; 0.03 C</td>
</tr>
<tr>
<td valign="top" align="justify" scope="row">Fe</td>
<td valign="top" align="justify">30.3 &#x00B1; 0.1 C</td>
<td valign="top" align="justify">34.1 &#x00B1; 0.8 BC</td>
<td valign="top" align="justify">43.9 &#x00B1; 0.3 ABC</td>
<td valign="top" align="justify">47.01 &#x00B1; 0.5 AB</td>
<td valign="top" align="justify">49.9 &#x00B1; 2.03 A</td>
<td valign="top" align="justify">28.1 &#x00B1; 8.17 ABC</td>
<td valign="top" align="justify">11.8 &#x00B1; 1.5D</td>
<td valign="top" align="justify">10.1 &#x00B1; 0.31 D</td>
</tr>
<tr>
<td valign="top" align="justify" scope="row">Ca</td>
<td valign="top" align="justify">13.1 &#x00B1; 0.2 E</td>
<td valign="top" align="justify">31.4 &#x00B1; 0.6 C</td>
<td valign="top" align="justify">39.82 &#x00B1; 0.4 B</td>
<td valign="top" align="justify">49.60 &#x00B1; 1.2 A</td>
<td valign="top" align="justify">37.4 &#x00B1; 0.7 B</td>
<td valign="top" align="justify">18.7 &#x00B1; 0.1 D</td>
<td valign="top" align="justify">17.8 &#x00B1; 0.9D</td>
<td valign="top" align="justify">14.07 &#x00B1; 0.3 E</td>
</tr>
<tr>
<td valign="top" align="justify" scope="row">Mg</td>
<td valign="top" align="justify">7.10 &#x00B1; 0.6 E</td>
<td valign="top" align="justify">29.3 &#x00B1; 0.4 BC</td>
<td valign="top" align="justify">35.23 &#x00B1; 0.9 A</td>
<td valign="top" align="justify">30.9 &#x00B1; 0.3 ABC</td>
<td valign="top" align="justify">32.5 &#x00B1; 1.2A B</td>
<td valign="top" align="justify">25.7 &#x00B1; 1.2 C</td>
<td valign="top" align="justify">14.5 &#x00B1; 1.5D</td>
<td valign="top" align="justify">13.4 &#x00B1; 0.4 D</td>
</tr>
<tr>
<td valign="top" align="justify" scope="row">K</td>
<td valign="top" align="justify">34.7 &#x00B1; 0.5 B</td>
<td valign="top" align="justify">58.3 &#x00B1; 4.1 A</td>
<td valign="top" align="justify">61.34 &#x00B1; 2.01 A</td>
<td valign="top" align="justify">56.20 &#x00B1; 1.1 A</td>
<td valign="top" align="justify">47.3 &#x00B1; 0.8 AB</td>
<td valign="top" align="justify">30.07 &#x00B1; 4.7 B</td>
<td valign="top" align="justify">10.4 &#x00B1; 4.3C</td>
<td valign="top" align="justify">6.7&#x00B1;0.7 C</td>
</tr>
</tbody></table></table-wrap>
</sec>
</sec>
<sec sec-type="discussion">
<title>Discussion</title>
<p>Zinc is a trace element that performs a vital role in plant growth and development. However, at higher concentrations, it reduces seed germination, length of seedlings and stem as well as contents of chlorophyll, carotenoid, sugar, and amino acids (<xref ref-type="bibr" rid="r37">Todeschini et al. 2011</xref>, <xref ref-type="bibr" rid="r13">Gli&#x0144;ska et al. 2016</xref>). [REMOVED HYPERLINK FIELD]In this study, the effects of zinc toxicity on plant height, leaf length, number of leaves, root length, fresh weight, and nutrient content was observed. Our results indicated that high Zn concentrations inhibited seed germination as compared to the control. Previous studies found a negative impact of Zn on plant growth parameters. Current findings are in agreement with previous studies (<xref ref-type="bibr" rid="r18">Islam et al. 2014</xref>, <xref ref-type="bibr" rid="r13">Gli&#x0144;ska et al. 2016</xref>, <xref ref-type="bibr" rid="r3">Boi et al. 2020</xref>), in these studies, they reported that increased heavy metal concentration causes decrease in plant biomass and growth. Nonetheless, maize inoculated with <italic>B. cereus</italic> showed increases in seed germination, plant height and fresh weight as well as nutrient uptake as compared to control and uninoculated plants. Enhanced root growth results due to inoculation of <italic>B. cereus</italic> under higher concentrations of zinc and thus a positive impact of <italic>B. cereus</italic> on root growth was observed, which may be due to the stress tolerance capacity of <italic>B. cereus</italic> (<xref ref-type="bibr" rid="r15">Hassan 2018</xref>). Improvement in plant root development under zinc concentration resulted in an increase in nutrient uptake, which increased seed germination, plant height, leaf length, number of leaves, root length and plant fresh weight. Inoculated seeds showed an increase in leaf growth and number of leaves as compared to un-inoculated plants grown in the soil supplemented with zinc.</p>
<p>We argue that gibberellins play a vital role in plant growth development. Scientific data suggests that <italic>B. cereus</italic> helps the plant by producing different plant promoting hormones i.e gibberellic acid (GA). Therefore, the increase in some plant growth parameters due to inoculation of <italic>B. cereus</italic> might be because of production of certain plant promoting enzymes, which can stimulate seed germination by enhancing growth ability (<xref ref-type="bibr" rid="r10">Finch-Savage and Leubner-Metzger 2006</xref>, <xref ref-type="bibr" rid="r38">Tuan et al. 2018</xref>). Gibberellins increase leaf area by suppressing peroxidase secretion (<xref ref-type="bibr" rid="r7">de Souza and MacAdam  2001</xref>), and induce cell mitotic division (<xref ref-type="bibr" rid="r33">Takatsuka and Umeda 2014</xref>, <xref ref-type="bibr" rid="r11">Fonouni-Farde et al. 2019</xref>).[REMOVED HYPERLINK FIELD] Moreover, some researchers suggested that <italic>B. cereus</italic> induces production of indole acetic acid (IAA), which may help to increase root length, plant height, and leaf area (<xref ref-type="bibr" rid="r26">Shafi et al. 2017</xref>). Henceforth, phytohormones produced by <italic>B. cereus</italic> might have played vital role in maize growth. Zn uptake decreased in <italic>B. cereus-</italic>inoculated maize plants. Common logic suggests that microbes including <italic>Bacillus</italic> species have ability to convert Zn into smaller, inaccessible and immoveable form in the soil (<xref ref-type="bibr" rid="r25">Saravanan et al. 2004</xref>, <xref ref-type="bibr" rid="r20">Li et al. 2016</xref>). Another explanation for reduced Zn uptake is production of metal binding proteins in the rhizosphere. <italic>Bacillus cereus</italic> produces metal binding proteins to counter heavy metal toxicity and these proteins have ability to restrict phytoavailability of heavy metals (<xref ref-type="bibr" rid="r18">Islam et al. 2014</xref>). We also demonstrated the accumulation of macro and micronutrients in maize plant owing to <italic>B. cereus</italic>. <italic>Bacillus cereus</italic> showed increase uptake of Cu, Mn, Ni, Na, Cr, Fe, Ca, and Mg in maize plant. <xref ref-type="bibr" rid="r36">Tiwari et al. (2013)</xref> also demonstrated that <italic>Bacillus</italic> species can enhance the phytoavailbility of nutrients Fe, Cd, Pb, Cr, Ni, Cu.</p>
</sec>
<sec sec-type="conclusions">
<title>Conclusion</title>
<p>It is concluded from the present investigation that maize seeds inoculated with <italic>B. cereus,</italic> in the presence of 20 mg kg<sup>-1</sup> of zinc showed significant increases in seed germination, plant height, leaf length, number of leaves; however, higher concentrations of zinc in uninoculated seeds indicated reduction in plant growth. Furthermore, the uptake of zinc in maize is decreased in the presence of <italic>B. cereus</italic> in the soil, which reduces the mobility of zinc leading to lower zinc accumulation in the maize plant. Our study demonstrated the positive impact of <italic>B. cereus</italic> on maize growth at different levels of Zinc toxicity. The present investigation revealed that <italic>B. cereus</italic> inoculation can be used as bio-fertilizer in Zinc-stressed soil.</p>
</sec>
</body>
<back>
<ref-list>
<title>References</title>
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