Effects of Biochar and Phosphorus on Dry Matter and Uptake of Calcium, Magnesium, Iron, Zinc, Copper, and Manganese by Rapeseed in a Calcareous Soil

Authors

Department of Soil Science, Faculty of Agriculture, University of Tabriz, Tabriz, Iran.

Abstract

Background and Objectives
Phosphorus (P) is a macronutrient that its deficiency severely limits plant growth and production. Because of the complexity of P chemistry in soil, less than 30% of applied P fertilizer is absorbed by plants and the rest in the soil converts to unavailable forms. Organic matter can be applied to the soil to reduce soil P fixation and increase soil P bioavailability because organic matter and its decomposition products (e.g., organic acids) occupy the surfaces of phosphate adsorbents in soils and prevent the precipitation of phosphate compounds. During pyrolysis of organic material a complex mixture of P species is formed, which may include amorphous, semi-crystalline, and crystalline constituents, along with organic constituents. However, organic P forms will tend to disappear while inorganic P forms will subsequently be formed and crystallinity will increase with increasing pyrolysis temperature. The crystalline P minerals that have been identified in biochars include whitlockite [(Ca, Mg)3(PO4)2] pyrolysed from manure at 500 °C, dehydrated struvite (NH4MgPO4) produced from cattle manure and sewage sludge, and hydroxyapatite [Ca10(PO4)6(OH)2] made from slaughterhouse waste and from mixtures of that waste with either corn residue or wood. The crystallinity of hydroxyapatite was lower when corn residues or wood were added to the slaughterhouse waste and as result increased the soluble P fraction. To the best of the authors’ knowledge, the evidence to support the impact of biochar on P sorption and desorption in Iranian soils is scarce while taking account of the fact that P deficiency is dominant in approximately 72% of the arable soils. So, in this research, the effects of combined application of biochar pyrolysed at 300 ˚C and P fertilizer on dry matter and uptake of calcium (Ca), magnesium (Mg), iron (Fe), zinc (Zn), copper (Cu), and manganese (Mn) by rapeseed (Brassica napus L.), Hyola 308 cultivar, were studied in an alkaline loamy soil under greenhouse conditions.
 
Methodology
After being washed with deionized water, wheat straw samples were milled, sieved < 1 mm, and then were oven-dried at 60 ºC for 24 h. The biochars were produced by slow pyrolysis of wheat straw at 300 ºC for 1 h under argon (Ar) gas flow at the heating rate of 10 ºC per minute. The produced biochars were transported in plastic containers for later analysis. Afterward, a factorial experiment was done on the basis of a completely randomized design with three replications. The factors were organic matter at 5 levels (no organic matter application, wheat straw 2%, wheat straw 4%, biochar 2%, and biochar 4%) and phosphorous (P) fertilizer at 3 levels (0, 20, and 40 mg/kg) as triple superphosphate. After the plant harvesting, shoot dry matter and the concentration and content of Ca, Mg, Fe, Zn, Cu, and Mn in plant shoot were determined by Atomic Absorption Spectrophotometer.
 
Results
Wheat straw application significantly reduced rapeseed shoot dry matter compared to the control. At each level of wheat straw (2 and 4%), P application significantly increased shoot dry matter as compared to the control treatment. Under wheat straw application conditions, the using both levels of P (20 and 40 mg/kg) significantly increased shoot dry matter. This finding indicates the possible immobilization of P due to wheat straw application and the positive effect of P fertilizer under these conditions. Using biochar at both levels of 2 and 4 percent increased the rapeseed shoot dry matter by 46 and 56.5 percent, respectively, compared to the control. The combined application of straw and P reduced the Ca, Mg, Fe, and Cu uptake at both levels of biochar (2 and 4 %) compared to the control. However, the content of Zn and Mn increased at the biochar level of 2% compared to the control, but significantly decreased at the biochar level of 4% compared to the control.
 
Conclusion
According to the results obtained from this research, the use of biochar produced from wheat straw at the temperature of 300˚C increased the uptake of Fe, Zn, and Mn, which led to the improvement of the growth characteristics of rapeseed. In this research, the effect of biochar on the Cu concentration and content in shoot unlike other nutrients was negative. According to the results, the wheat straw drived biochar at 300 °C improved rapeseed plant growth characteristics and nutrients uptake except Cu. Also, application of biochar and P at 2% and 20 mg/kg levels, respectively, is recommended to reduce the consumptions of P fertilizer without yield reduction of rapeseed in under similar conditions. In addition, application of wheat straw at 2 and 4 % levels is not recommended and future research should be done at its lower levels. Finally, it was concluded that biochar may play an important role in soil fertility and plant production, so further research should continue.
 
 
Data Availability Statement
Data is available on reasonable request from the authors.
 
Acknowledgements
This paper is published as a part of a Master's thesis supported by the Vice Chancellor for Research and Technology of the University of Tabriz, Tabriz, Iran. The authors are thankful to the University of Tabriz for financial supports.
 
Conflict of interest
The authors declare no conflict of interest.
 
Ethical considerations
The authors avoided data fabrication, falsification, plagiarism, and misconduct.

Keywords


Alburquerque, J.A., Salazar. P., Barrón, V., Torrent, J., Campillo, M.d.C., Gallardo, A. & Villar, R. (2013). Enhanced wheat yield by biochar addition under different mineral fertilization levels. Agronomy for Sustainable Development, 33(3), 475–484.
Amin, E.A.Z. (2018). Phosphorus dynamics and corn growth under applications of corn stalks biochar in a clay soil. Arabian Journal of Geosciences, 11(14), 379–396
Antón‐Herrero, R., Vega‐Jara, L., García‐Delgado, C., Mayans, B., Camacho‐Arévalo, R., Moreno‐Jiménez, E., and Eymar, E. (2022). Synergistic effects of biochar and biostimulants on nutrient and toxic element uptake by pepper in contaminated soils. Journal of the Science of Food and Agriculture, 102, 167–174. 
Azimzadeh, Y., Najafi, N., Reyhanitabar, A., Oustan, S. & Khataee, A. (2020). Effects of phosphate loaded LDH-biochar/hydrochar on maize dry matter and P uptake in a calcareous soil. Archives of Agronomy and Soil Science, 67(12), 1649–1664.
 
Beesley, L., & Dickinson, N. (2011). Carbon and trace element fluxes in the pore water of an urban soil following greenwaste compost, woody and biochar amendments, inoculated with the earthworm (Lumbricus terrestris). Soil Biology and Biochemistry, 43, 188–196.
 Carter, S., Shackley, S., Sohi, S., Suy, T.B. & Haefele, S. (2013). The impact of biochar application on soil properties and plant growth of pot grown lettuce (Lactuca sativa) and cabbage (Brassica chinensis). Agronomy, 3, 404–418.
Crowly, D.E., Romheld, V., Marschner, H. & Szaniszli, P.J. (1992). Root microbial effects on plant iron uptake from sidrophores and phito sidrophores. Plant and Soil, 142, 1–7.
Dong, X., Ma, L.Q. & Li. Y. (2011). Characteristics and mechanisms of hexavalent chromium removal by biochar from sugar beet tailing. Journal of Hazardous Materials, 190, 909–915.
Duku, M.H., Gu, S. & Hagan, E.B. (2011). Biochar production potential in Ghana- a review. Renewable and Sustainable Energy Reviews, 15, 3539–3551.
Frišták, V. & Soja, G. ( 2015). Effect of wood-based biochar and sewage sludge amendments for soil phosphorus availability. Nova Biotechnologica Et Chimica, 14, 104–115.
Gee, G.W., Or, D. )2002(. Particle size analysis. Pp. 255–293. In: Dane, J.H., Topp, G.C. (Eds.), Methods of soil analysis. Part 4. Physical methods. Soils Science Society of America, Book Series No. 5, Madison, WI., USA.
Ghadam Kheir, E., Nadian, H. & Jafari, S. (2017). The effect of biochar and vermicompost on concentration of some micronutrients in canola under salinity stress. Pp.1–6. In: 15th Iranian Soil Science Congress,28 -30August. 2017, Isfahan-Iran (In Persian with English abstract).
Havlin, J.L., Beaton, J.D., Tisdale, S.L & Nelson, W.L. (2016). Soil fertility and fertilizers. Sixth Edition,  Academic Press, Soil Science Society of America. Madison, WI., USA.
Hoseini, Y., Homaee, M., Karimian, N.A & Saadat, S. (2009). The effects of phosphorus and salinity on growth, nutrient concentrations, and water use efficiency in canola (Brassica napus L.). Journal of Agricultural Research 8, 1–18. (In Persian with English abstract).
Jones, J.R. (2001). Laboratory guide for conducting soil tests and plant analysis. CRC Press, Boca Raton, FL., USA.
Karimi, E., Shirmardi, M., Dehestani Ardakani, M., Gholamnezhad, J. & Zarebanadkouki, M. (2020). The effect of humic acid and biochar on growth and nutrients uptake of calendula (Calendula officinalis L.). Communications in Soil Science and Plant Analysis, 51, 1658–1669.‏
Khanmohammadi, Z., Afyuni, M. & Mosaddeghi, M.R. (2017). Effect of sewage sludge and its biochar on chemical properties of two calcareous soils and maize shoot yield. Archives of Agronomy and Soil Science, 63, 198–212.
Kuppusamy, S., Thavamani, P., Megharaj, M., Venkateswarlu, K. & Naidu, R. (2016). Agronomic and remedial benefits and risks of applying biochar to soil: current knowledge and future research directions. Environment International, 87, 1–12.
Lehmann, J. & Joseph S. (2015). Biochar for Environmental Management: Science, Technology and Implementation. Second  Edition, Academic Press, London, UK.  
Lehmann, J., Kem, D., German, L., McCann, J., Martis, G.C. & Moreira, L. (2003). Soil fertility and production potential. Chapter 6. Pp. 105–124. In: Lehmann J, Kern DC, Glaser B, W. I. Woods (Eds). Amazonian dark earths: origin, properties, management. Kluwer Academic, Dordrecht, the Netherlands.
Lindsay, W.L. & Norvell, W.A. (1978). Development of a DTPA soil test for zinc, iron, manganese, and copper. Soil Science Society of America Journal, 42, 421–428.
Lindsay, W.L., Vlek, P.L. & Chien, S.H. (1989). Phosphate Minerals. Pp. 1089–1130. In:  Dixeon, J.B. &Weed SB (Eds). Minerals in soil environments. Secondth Edition. SSSA Book Series No. 1, Madison, WI. USA.
Maghsoodi, M.R., Najafi, N., Reyhanitabar, A. & Oustan, S. (2024). Effects of biochar, hydrochar, zeolite, and hydroxyapatite nanorods as urea carriers on some agronomical traits and water use efficiency of rice plant. Journal of Soil Science and Plant Nutrition, https://doi.org/10.1007/s42729-024-02143-8
Marschner, P. (2012). Marschner’s mineral nutrition of higher plants. Second Edition, Academic Press, London, UK.
Mbah, C., Njoku, C., Okolo, C., Attoe, E. & Osakwe, U. (2017). Amelioration of a degraded ultisol with hardwood biochar: effects on soil physico-chemical properties and yield of cucumber (Cucumis sativus L.). African Journal of Agricultural Research, 12, 1781–1792.
Molla, M.S., Akhter, M., Maniruzzaman, M., Lipi, N.J., Rabiul, A. & Tisam, A. (2017). Response of biochar to plant nutrients and yield of Amaranthus tricolor. International Journal of Innovative Research, 2, 13–17.
Moreno-Jiménez, E., Fernández, J.M., Puschenreiter, M., Williams, P.N. & Plaza, C. ( 2016). Availability and transfer to grain of As, Cd, Cu, Ni, Pb and Zn in a barley agri-system: Impact of biochar, organic and mineral fertilizers. Agriculture, Ecosystems and Environment, 219, 171–178.
Nelson, D.W. & Sommers, L.E. (1996). Total carbon, organic carbon, and organic matter. Pp. 961–1010. In: Methods of soil analysis. Sparks, D.L, et al. (EDs) Part 3. Chemical methods. Soil Science Society of America, American Society of Agronomy, Madison, WI., USA.
Olsen, S.R. & Sommer, L.E. (1982). Phosphorus. Pp. 403–430. In: Page, A.L, Miller, R.H and Keeney, D.R. (Eds). Methods of soil analysis: Part 2. Chemical and Microbiological Properties. SSSA, Madison, WI., USA.
Ouda, B.A. & Mahadeen, A.Y. (2008). Effect of fertilizers on growth, yield, yield components, quality and certain nutrient contents in broccoli (Brassica oleracea). International Journal of Agriculture and Biology ,10, 627–32.
Park, J.H., Choppala, G.K., Bolan, N.S, Chung, J.W & Chuasavathi, T., 2011. Biochar reduces the bioavailability and phytotoxicity of heavy metals. Plant and Soil, 348, 439–451
Price, G., 2006. Australian soil fertility manual. Third Edition, Fertilizer Industry Federation of Australia Inc. and CSIRO Publishing, Collingwood, Victoria, Australia.
Puga, A., Abreu, C., Melo, L. & Beesley, L. (2015). Biochar application to a contaminated soil reduces the availability and plant uptake of zinc, lead and cadmium. Journal of Environmental Management ,159, 86–93.
Reyhanitabar, A., Frahadi, E., Ramezanzadeh, H. & Oustan, S. (2020). Effect of pyrolysis temperature and feedstock sources on physicochemical characteristics of biochar. Journal of Agricultural Science and Technology, 22, 547–561
Rhoades, J. (1996). Salinity: electrical conductivity and total dissolved solids. Pp. 417–435. In: Sparks, D.L et al. (Eds.). Methods of soil analysis, Part 3. Chemical methods. SSSA, Madison, WI., USA.  
Shahbazi, K. & Besharati, H.( 2013). Overview of agricultural soil fertility status of Iran. Journal of Land Management, 1, 1–15. (In Persian with English abstract).
Singh, B., Camps-Arbestain, M. & Lehmann, J.( 2017). Biochar: A guide to analytical methods. First Edition, Academic Press, CSIRO Publishing.
Song, W. & Guo, M. (2012). Quality variations of poultry litter biochar generated at different pyrolysis temperatures. Journal of Analytical and Applied Pyrolysis, 94, 138–145.
Sousa, A., & Figueiredo, C., (2016). Sewage sludge biochar: effects on soil fertility and growth of radish. Biological Agriculture and Horticulture, 32, 127–138.
Sposito, G., Lund, L.J, & Chang, A.C. (1982). Trace metal chemistry in arid zone field soils amended with sewage sludge: I. Fractionation of Ni, Cu, Zn, Cd and Pb in soil phases. Soil Science Society of America Journal, 46, 260–264.
Tavajjoh, M., Karimian, N.A., Ronaghi, A., Yasrebi, J., Hamidi, R., & Olama, V. (2016). Yield, yield components and seed quality of two rapeseed cultivars as affected by different levels of phosphorus and boron under greenhouse conditions. Journal of Science and Technology of Greenhouse Culture, 6, 99–113. (In Persian with English abstract).
Thomas,  G.W. (1996). Soil pH and soil acidity. pp. 475-490. In: Sparks, D.L et al., (Eds). Methods of soil analysis. Part 3. Chemical methods. Soil Science Society of America, American Society of Agronomy, Madison, WI., USA..
Vahedi, R., Rasouli-Sadaghiani, M.H., Barin, M. & Vetukuri, R.R. (2022). Effect of biochar and microbial inoculation on P, Fe, and Zn bioavailability in a calcareous soil. Processes, 10, 343–357‏
Wang, T., Camps-Arbestain, M., Hedley, M. & Bishop, P. (2012). Predicting phosphorus bioavailability from high-ash biochars. Plant and Soil, 357, 173–187.
Xu, X., Cao, X. & Zhao, L. (2013). Comparison of rice husk-and dairy manure-derived biochars for simultaneously removing heavy metals from aqueous solutions: role of mineral components in biochars. Chemosphere, 92(8), 955–961.
Zemanová, V., Břendová, K., Pavlíková, D., Kubátová, P. & Tlustoš, P. ( 2017). Effect of biochar application on the content of nutrients (Ca, Fe, K, Mg, Na, P) and amino acids in subsequently growing spinach and mustard. Plant, Soil and Environment, 7, 322–327.
 Zolfi Bavariani, M., Ronaghi, A., Karimian, N., Yasrebi, J. & Ghasemi, R. ( 2017). Influence of biochars prepared from poultry manure on phosphorus availability and recovery in a calcareous soil. Journal of Water and Soil Science,  21, 23–35. (In Persian with English abstract).