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      Potential role of compost mixed biochar with rhizobacteria in mitigating lead toxicity in spinach

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          Abstract

          Consumption of heavy metals, especially lead (Pb) contaminated food is a serious threat to human health. Higher Pb uptake by the plant affects the quality, growth and yield of crops. However, inoculation of plant growth-promoting rhizobacteria (PGPR) along with a mixture of organic amendments and biochar could be an effective way to overcome the problem of Pb toxicity. That’s why current pot experiment was conducted to investigate the effect of compost mixed biochar (CB) and ACC deaminase producing PGPR on growth and yield of spinach plants under artificially induced Pb toxicity. Six different treatments i.e., control, Alcaligenes faecalis (PGPR1), Bacillus amyloliquefaciens (PGPR2), compost + biochar (CB), PGPR1 + CB and PGPR2 + CB were applied under 250 mg Pb kg -1 soil. Results showed that inoculation of PGPRs ( Alcaligenes faecalis and Bacillus amyloliquefaciens) alone and along with CB significantly enhanced root fresh (47%) and dry weight (31%), potassium concentration (11%) in the spinach plant. Whereas, CB +  Bacillus amyloliquefaciens significantly decreased (43%) the concentration of Pb in the spinach root over control. In conclusion, CB +  Bacillus amyloliquefaciens has the potential to mitigate the Pb induced toxicity in the spinach. The obtained result can be further used in the planning and execution of rhizobacteria and compost mixed biochar-based soil amendment.

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          Biochar as a sorbent for contaminant management in soil and water: a review.

          Biochar is a stable carbon-rich by-product synthesized through pyrolysis/carbonization of plant- and animal-based biomass. An increasing interest in the beneficial application of biochar has opened up multidisciplinary areas for science and engineering. The potential biochar applications include carbon sequestration, soil fertility improvement, pollution remediation, and agricultural by-product/waste recycling. The key parameters controlling its properties include pyrolysis temperature, residence time, heat transfer rate, and feedstock type. The efficacy of biochar in contaminant management depends on its surface area, pore size distribution and ion-exchange capacity. Physical architecture and molecular composition of biochar could be critical for practical application to soil and water. Relatively high pyrolysis temperatures generally produce biochars that are effective in the sorption of organic contaminants by increasing surface area, microporosity, and hydrophobicity; whereas the biochars obtained at low temperatures are more suitable for removing inorganic/polar organic contaminants by oxygen-containing functional groups, electrostatic attraction, and precipitation. However, due to complexity of soil-water system in nature, the effectiveness of biochars on remediation of various organic/inorganic contaminants is still uncertain. In this review, a succinct overview of current biochar use as a sorbent for contaminant management in soil and water is summarized and discussed.
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            Black Carbon Increases Cation Exchange Capacity in Soils

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              The forms of alkalis in the biochar produced from crop residues at different temperatures.

              The forms of alkalis of the biochars produced from the straws of canola, corn, soybean and peanut at different temperatures (300, 500 and 700°C) were studied by means of oxygen-limited pyrolysis. The alkalinity and pH of the biochars increased with increased pyrolysis temperature. The X-ray diffraction spectra and the content of carbonates of the biochars suggested that carbonates were the major alkaline components in the biochars generated at the high temperature; they were also responsible for the strong buffer plateau-regions on the acid-base titration curves at 500 and 700°C. The data of FTIR-PAS and zeta potentials indicated that the functional groups such as -COO(-) (-COOH) and -O(-) (-OH) contained by the biochars contributed greatly to the alkalinity of the biochar samples tested, especially for those generated at the lower temperature. These functional groups were also responsible for the negative charges of the biochars. Copyright © 2010 Elsevier Ltd. All rights reserved.
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                Author and article information

                Contributors
                shahfahad@uoswabi.edu.pk
                rahulmedcure@gmail.com
                sd96850@gmail.com
                Journal
                Sci Rep
                Sci Rep
                Scientific Reports
                Nature Publishing Group UK (London )
                2045-2322
                22 July 2020
                22 July 2020
                2020
                : 10
                : 12159
                Affiliations
                [1 ]ISNI 0000 0001 0228 333X, GRID grid.411501.0, Department of Soil Science, Faculty of Agricultural Sciences and Technology, , Bahauddin Zakariya University, ; Multan, 60800 Punjab Pakistan
                [2 ]ISNI 0000 0004 4657 4747, GRID grid.502337.0, Department of Agriculture, , The University of Swabi, ; Khyber Pakhtunkhwa, Pakistan
                [3 ]ISNI 0000 0004 1790 4137, GRID grid.35155.37, College of Plant Sciences and Technology, , Huazhong Agriculture University, ; Wuhan, China
                [4 ]ISNI 0000000122191520, GRID grid.7112.5, Department of Agrochemistry, Soil Science, Microbiology and Plant Nutrition, Faculty of AgriSciences, , Mendel University in Brno, ; Zemedelska 1, 61300 Brno, Czech Republic
                [5 ]ISNI 0000 0001 0118 0988, GRID grid.4994.0, Institute of Chemistry and Technology of Environmental Protection, , Brno University of Technology, Faculty of Chemistry, ; Purkynova 118, 62100 Brno, Czech Republic
                Article
                69183
                10.1038/s41598-020-69183-9
                7376197
                32699323
                c024160b-f97a-4dc4-8804-fe17a6670ce6
                © The Author(s) 2020

                Open Access This article is licensed under a Creative Commons Attribution 4.0 International License, which permits use, sharing, adaptation, distribution and reproduction in any medium or format, as long as you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons license, and indicate if changes were made. The images or other third party material in this article are included in the article’s Creative Commons license, unless indicated otherwise in a credit line to the material. If material is not included in the article’s Creative Commons license and your intended use is not permitted by statutory regulation or exceeds the permitted use, you will need to obtain permission directly from the copyright holder. To view a copy of this license, visit http://creativecommons.org/licenses/by/4.0/.

                History
                : 1 May 2020
                : 30 June 2020
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                © The Author(s) 2020

                Uncategorized
                abiotic,environmental impact,bacterial secretion
                Uncategorized
                abiotic, environmental impact, bacterial secretion

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