Document Type : Research Paper
Authors
1 Master Student, Department of Soil Science, University of Jiroft
2 Assistant Professor, Department of Soil Science, Jiroft University.
Abstract
Introduction: Biochar which is used as a soil amendment, is defined as a stable-carbon-rich product, and can endure in soil for thousands of years. Biochar is produced from biomass such as wood, manure, leaves, and other agricultural waste via pyrolysis, by heating at temperatures 300-1000°C in a closed container with little or no available air. Biochar, because of its potential to improve the physical and chemical properties of soil, is known as an effective soil amendment. Different types of organic waste particularly the residual of plants can be used as feedstock to produce biochar, but it's important to assess the Biochar properties to apply it as a soil amendment.
Materials and Methods: In this study, we investigated some physicochemical properties of biochar of pistachio ́s waste, produced in different pyrolysis temperatures. The pistachio harvesting waste was collect from pistachio orchards in Zarand city, which mainly consisted of the green husk, pistachio cluster, leaves and small amounts of nut and woody shell and thin wood waste. A series of biochar were produced from pistachio waste by slow pyrolysis at different temperatures (300, 450, 600 and 750◦C, for 2 h) to find out the best temperature for the preparation of biochar from this matter. After preparation of biochars, their physicochemical properties including pH, electrical conductivity (EC), bulk density, particle density, biochar yield (mass of the biochar to dry mass of feedstock), ash content, water holding capacity (WHC) and stable-OC, were measured.
Results and Discussion: In general, optimal biochar is the one that its yield, water holding capacity and stable organic carbon (OC) are higher and its electrical conductivity is lower. The results showed that as temperature increased from 300 to 750◦C, biochar yield and bulk density of the biochar decreased. In contrast, with increasing the temperature, pH, EC, particle density, ash content and stability of OC were increased. The electrical conductivity (EC) in the feedstock material was about 5.8 dS/m and their conversion to biochar and the increasing of pyrolysis temperature, increased the salinity of this material. The highest of EC was observed at 750◦C which was more than 2.5 and 6 times than in at temperature 300◦C and in the feedstock, respectively. The biochars produced at all temperatures have a high pH which it may be considered as an amendment for the reclamation of acidic soils, however the high salinity of the biochars could be a negative factor for plant growth. Also, as the pyrolysis temperature increased, the amount of ash in the biochar increased. The highest of ash content was observed at the highest temperature (58.3%) which was about 460% more than in the feedstock. Stable organic carbon in biochars produced at temperatures of 300, 450, 600 and 750◦C was about 49, 206, 227 and 227% higher than that of raw pistachio residue, respectively; and the percentage of yield of biochar at 300◦C was more than 65% higher than that of 750◦C. Although the WHC of biochars in different temperatures had no clear trend; it was slightly lower at a temperature of 450◦C in compared to the other temperatures. Also, in a trend, the biochars prepared at the higher temperatures showed higher stable-OC but lower yield.
Conclusion: The temperature of the pyrolysis process is a key factor in the yield, quality, and physicochemical properties of the pistachio’s waste biochar. In the context of carbon sequestration as an environmental aspect and more yield of biochar as an economic aspect in the production of biochar and application of this matter in the soil, our results recommend the preparation of biochar from pistachio ́s waste, at temperature 450◦C or 600◦C, or a temperature in between. In the previous studies it has also been shown, the biochars produced at temperatures of 450◦C or higher was most likely to improve soil drainage and make more water available to plants but it needs more energy in the production procedure, while ones produced at lower temperatures could induce soil water repellency.
Temperature of pyrolysis process is a key factor on yield, quality, and physicochemical properties of the pistachio’s waste biochar. In context of carbon sequestration as an environmental aspect and more yield of biochar as an economic aspect in production of biochar and application of this matter in soil, our results recommend the preparation of biochar from pistachio ́s waste, at temperature 450◦C or 600◦C, or a temperature in between. In the previous studies it has also been shown, the Biochars produced at temperatures of 450◦C or higher was most likely to improve soil drainage and make more water available to plants but it needs more energy in production procedure, while ones produced at lower temperatures could may induce soil water repellency.
Keywords
References
- Abrishami, M.H. 1994. Iranian Pistachio (Historical Recognition). University Publication Center, Tehran, 673p. (in Persian).
- Al-Wabel, M., Al-Omran, A., El-Naggar, A.H., Nadeem, M., and Usman, A.R. 2013. Pyrolysis temperature induced changes in characteristics and chemical composition of biochar produced from Conocarpus wastes. Bioresource Technology, 131: 374-379.
- Aminian, A. and ShakerArdakani, A. 2008. Pistachio waste and its applications. Publication Center of Iranian Pistachio Research Institute. (in Persian).
- Amonette, J. E. and Joseph, S. 2009. Characteristics of biochar micro chemical properties. Chapter 3: In: Lehmann, J. and Joseph, S. (Eds), Biochar for environmental management: science and Earth scan, London, PP. 33–52.
- Aston, S., Doerr, S. and Street-Perrott, A. The impacts of pyrolysis temperature and feedstock type on biochar properties and the effects of biochar application on the properties of sandy loam. EGU General Assembly 2013, held 7-12 April, 2013 in Vienna, Austria, ID. EGU2013-1108.
- Blake, G.R., and Hartge, K.H. 1986. Particle density. In: Klute, A. (ed). Methods of soil Analysis- Part 1. Physical and Mineralogical Methods. 2nd Agron. Monogr, 9. ASA and SSSA, Madison, WI. PP. 377-382.
- Cao, X. and Harris, W. 2010. Properties of dairy manure derived biochar pertinent to its potential use in remediation. Bioresource Technology, 101: 5222–5228.
- Downie, A., Crosky, A., and Munroe, P. 2009. Physical properties of biochar. In: Lehmann, J. and Joseph, S. (Eds.), Biochar for Environmental Management: Science and Technology. Earth scan, London, PP. 13–32.
- Flint, A.L., and Flint, L.E. 2002. Particle density. In: Dane, J.H. and Topp, G.C. (Eds.), Methods of soil Analysis- Part 4. Physical Methods- ASA and SSSA Book Series No. 5. Soil Sci, Madison, PP. 299-240.
- Forogh Amari, N. 1997. Determination of the nutritional value and digestibility of soft pistachio shells. Master thesis, Isfahan University of Technology (in Persian).
- Glaser, B., Lehmann, J., and Zech, W. 2002. Ameliorating physical and chemical properties of highly weathered soils in the tropics with charcoal - a review. Biology and Fertility of Soils, 35 (4): 219–230.
- Gundale, M.J. and Deluca, T.H. Temperature and substrate influence the chemical properties of charcoal in the ponderosa pine/Douglas-fir ecosystem, Forest. Ecology and Management, 231: 86-93.
- Karhu, K., Mattila, T., Bergstrom, I., and Regina, K. 2011. Biochar addition to agricultural soil increased CH4 uptake and water holding capacity – Results from a short-term pilot field study. Agriculture, Ecosystems and Environment, 140(1): 309–313.
- Kercher, A.K. and Nagle, D.C. 2002. Evaluation of carbonized medium-density fiberboard for electrical applications. Carbon, 40: 1321–1330.
- Khadem, A., Fekri, M., and Mahmudbadi, M. 2016. Biochar effect of pistachio waste at two different temperatures to removal fluoride from aqueous. 4th international congress of structure, architecture and urban development. ICSAU04_2118.
- Khanmohammadi, Z., Afyuni, M., and Mosaddeghi, M.R. 2015a. Effect of Pyrolysis Temperature on Chemical Properties of Sugarcane Bagasse and Pistachio residues Biochar. Applied Soil Research, 3(1): 1-13 (in Persian).
- Khanmohammadi, Z., Afyuni, M., and Mosaddeghi, M.R. 2015b. Effect of pyrolysis temperature on chemical and physical properties of sewage sludge biochar. Waste Management and Research, 33(3):275-283.
- Kookana, R.S., Sarmah, A.K., Van Zwieten, L., Krull, E., and Singh, B. 2011. Biochar application to soil: Agronomic and environmental benefits and unintended consequences. Advances in Agronomy, 112: 103-143.
- Kwon, S. and Pignatello, J.J. 2005. Effect of natural organic substances on the surface and adsorptive properties of environmental black carbon (char): pseudo pore blockage by model lipid components and its implications for N2-probed surface properties of natural sorbents. Environmental Science and Technology. 39(20):7932-7939.
- Laird, D.A., Fleming, P., Davis, D.D., Horton, R., Wang, B., and Karlen, D.L. 2010. Impact of biochar amendments on the quality of a typical Midwestern agricultural soil. Geoderma, 158(3): 443–449.
- Lehmann, J., Gaunt, J., and Rondon, M. 2006. Bio-char sequestration in terrestrial ecosystems: A review. Mitigation and Adaptation Strategies for Global Change, 11(2): 403–427.
- Lehmann, J., Kern, D., German, L., McCann, J., Martins, G.C., and Moreira, A. 2003. Soil fertility and production potential. In: Lehmann, J., Kern, D.C., Glaser, B., and Wodos, W.I. (Eds), Amazonian Dark Earths: Origin, Properties, and Management. Kluwer Academic Publishers, PP. 105-124.
- Liang, B., Lehmann, J., Solomon, D., Kinyangi, J., Grossman, J., O'Neill, B., Skjemstad, J.O., Thies, J., Luizão F.J., Petersen, J., and Neves, E.G. 2006. Black carbon increases cation exchange capacity in soils. Soil Science Society of America Journal, 70(5): 1719–1730.
- Lua, A.C. and Yang, T. Effects of vacuum pyrolysis conditions on the characteristics of activated carbons derived from pistachio-nut shells. Journal of Colloid and Interface Science, 276(2): 364–372.
- Marshall, J., Muhlack, R., Morton, B.J., Dunnigan, L., Chittleborough, D., and Kwong, C.W. 2019. Pyrolysis Temperature Effects on Biochar–Water Interactions and Application for Improved Water Holding Capacity in Vineyard Soils. Soil System, 3 (27): 1-14.
- Novak, J.M., Busscher, W.J., Laird, D.L., Ahmedna, M., Watts, D.W., and Niandou, M.A.S. 2009. Impact of biochar amendment on fertility of a Southeastern Coastal Plain soil. Soil Science, 174: 105–112.
- Nowroozi, M., Tabatabaei, S.H., Nouri, M.R., and Motaghian, H. 2017. Short-term effects of biochar produced from date palms leaves on moisture retention in sandy loam soil. Journal of Water and Soil Resources Conservation, 6 (2): 137150. (In Persian).
- Oberlin, A. 2002. Pyrocarbons. Carbon, 40: 7–24.
- Schumacher, B.A. 2002. Methods for the determination of total organic carbon (TOC) in soils and sediments. Ecological Risk Assessment Support Center, PP. 1-23.
- Singh, A., Biswas, A.K., Singhai, R., Lakaria, L.B., and Dubey, A.K. 2015. Effect of pyrolysis temperature and retention time on mustard straw derived biochar for soil amendment. Journal of Basic and Applied Scientific Research, 5: 31-37.
- Singh, B., Mei Dolk, M., Shen, Q., and Camps-Arbestain, M. 2017. Biochar pH, electrical conductivity and liming potential. In: Biochar: A Guide to Analytical Methods, Chapter 3, Singh, B., Camps-Arbestain, M., and Lehmann J., (Eds.). Publisher CSIRO, PP. 23-38.
- Sohi, S.P., Krull, E., Lopez-Capel, E., and Bol, R. 2010. A review of biochar and its use and function in soil. Advances in Agronomy, 105: 47-82.
- Song, W. and Guo, M. 2012. Quality variations of poultry litter biochar generated at different pyrolysis temperatures. Journal of Analytical and Applied Pyrolysis, 94: 138-145.
- Taghizadeh-Alisaraei, A., AlizadehAssar, H., Ghobadian, B., and Motevali, A. 2017. Potential of biofuel production from pistachio waste in Iran. Renewable and Sustainable Energy Reviews, 72: 510-522.
- Uchimiya, M., Wartelle, L.H., Klasson, K.T., Fortier, C.A., and Lima, I.M. Influence of pyrolysis temperature on biochar property and function as a heavy metal sorbent in soil. Journal of Agriculture and Food Chemistry, 59: 2501–2510.
- Van Zwieten, L., Kimber, S., Morris, S., Chan, K., Downie, A., Rust, J., Joseph, S., and Cowie, A. 2010. Effects of biochar from slow pyrolysis of papermill waste on agronomic performance and soil fertility. Plant and Soil, 327: 235-246.
- Verheijen, F.G.A., Jeffery, S., Bastos, A.C., van der Velde, M., and Diafas, I. Biochar application to soils – A Critical Scientific Review of Effects on Soil Properties, Processes and Functions. EUR 24099 EN, Office for the Official Publications of the European Communities, Luxembourg, 149pp.
- Wang, B., Gao, A.R., Zimmerman, Y.Li., Mad, L., Harris, W.G., and Migliaccio, K.W. 2015. Physicochemical and sorptive properties of biochars derived from woody and herbaceous biomass. Chemosphere, 134: 257-262.
- Woolf, D.J., Amonette, E., and Street-Perrott, F.A. 2010. Sustainable biochar to mitigate global climate change. Nature Communications, 1: 1-9.
- Yang, H., and Sheng, K. 2012. Characterization of biochar properties affected by different pyrolysis temperatures using visible near infrared spectroscopy. International Scholarly Research Network Spectroscopy, ID: 712837.
- Yuan, J.H. and Xu, R.K. 2011. The amelioration effects of low temperature biochar generated from nine crop residues on an acidic Ultisol. Soil Use Management, 27: 110–115.
- Yuan, J.H., Xu, R.K., and Zhang, H. 2011. The forms of alkalis in the biochar produced from crop residues at different temperatures. Bioresource technology, 102(3): 3488-3497.
Zhao, S.X., Ta, N., and Wang, X.D. 2017. Effect of temperature on the structural and physicochemical properties of biochar with apple tree branches as feedstock material. Energies, 10, 1293: 1-15.