Open access

Introductory Chapter: Is Biochar Safe?

Written By

Ahmed A. Abdelhafez, Xu Zhang, Li Zhou, Guoyan Zou, Naxin Cui, Mohammed H.H. Abbas and Mahdy H. Hamed

Submitted: 06 January 2020 Published: 22 July 2020

DOI: 10.5772/intechopen.91996

From the Edited Volume

Applications of Biochar for Environmental Safety

Edited by Ahmed A. Abdelhafez and Mohammed H. H. Abbas

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1. Introduction

Biochar is a carbon-rich product resulted from the pyrolysis of organic biomass in the absence of oxygen or at relatively low-oxygen conditions [1]. Such a process transforms the easily oxidized carbon fractions presented in the organic residues into more stable forms [2] that can persist in soils for years, probably 7 [3] to 10 [4] years. This amendment reduces, therefore, the emissions of greenhouses gases [5] and can be considered as a climate change mitigation [6]. On the other hand, required amounts of this conditioner to improve soil productivity might be less comparable with compost or other organic amendments on the long run. Accordingly, biochar is presented as a promising soil amendment of high economic and environmental value. It is also named as “the black diamond” [7]. However, many environmental aspects should be considered while using this amendment. The first one considers its manufacturing process. During the pyrolysis process of biochar, significant emissions of CO2 are produced, and this probably raises the levels of greenhouse gases (GHGs) in air [8]. The second important issue is related to the biochar degradation in soil. Under warm climate conditions, its degradation was reported to be relatively high [9, 10], and therefore, further emissions of greenhouse gases might take place from biochar-amended soils. The third topic concerns ethylene, which is a by-product of the pyrolysis process of biochar [11]. This gas is increased considerably in biochar-amended soils to suppress several soil microbial processes [12]. Many researches considered this point a positive one that increases the stability of biochar in soil while reduces the emissions of greenhouse gases produced upon its degradation in soil [13], yet biochar affects negatively soil biota [14]. This is because this product contains a small part of bioavailable C [15] as the labile C is already degraded [16]. Thus, the sustainability of crop production in soil referred by soil health (or soil quality) which “reflects the capacity of a soil to provide ecosystem services” [17] may also be affected. Soil biota not only affects the physical and chemical properties of soil but also improves plant health [18]. Further pros and cons of amending soils with biochar will be discussed briefly in the following section.

Several studies demonstrated the positive impacts of amending soils with biochar on increasing crop productivity. For example, amending soils with biochar improves significantly macro- and micronutrients availability [9], in spite of the fact that many biochar additives have an alkaline nature [19], and consequently raises soil pH [7, 8, 9, 10, 11, 12, 13, 14, 15, 16, 17, 18, 19, 20]. Nevertheless, soil nutrients strongly are adsorbed on biochar which serves as a slow release fertilizer [21]. It is then thought that the better utility of biochar can be detected on acid soils, rather than alkaline or calcareous soils. Moreover, this amendment reduces NO3 loss through leaching as well as the gaseous loss through release of nitrous oxide [22]; hence; this amendment can positively enhance plant growth [23]. Also, this product, which is characterized by its porous structure and high surface area [24], recorded indirect impacts on soil physical characteristics; for example, this amendment increases significantly water retention [10, 11, 12, 13, 14, 15, 16, 17, 18, 19, 20, 21, 22, 23, 24, 25], hydraulic conductivity [26], and the total porosity of sandy soils while decreasing soil bulk density [27]. However, the impacts of amending soils with biochar are not always the same and depend mainly on the characteristics of the used biochar such as its grain size and pyrolysis temperature. According to [28], fine biochar decreases soil hydraulic conductivity, while the coarse biochar (particles were coarser than sand) did not affect the hydraulic conductivity of soils. Also, the pyrolysis temperature seems to have a significant impact on ash content in biochar, its pH, EC, and basic functional groups as well as carbon stability which increases in biochar with increasing pyrolysis temperature [29]. Generally, the effect of biochar on soil physical properties was comparable with the effect of compost [30]. On the other hand, other reports indicate that this amendment recorded unfavorable changes in chemical, physical, and biological properties of soil and consequently reduced crop yield [31]. Also, its application to soil hinders root penetration into soil depth [32]. Moreover, its negative impacts were also considerable on earthworm populations even on the short range [33]. It seems that the environmental and health risks due to biochar applications in agricultural soils are not well explored.

Another positive point for using biochar as a soil conditioner is related to its success to mitigate salinization of arable lands [34]. Additionally, biochar plays positive significant impacts on controlling the contaminants presented in water and soils [35, 36]. However, many contaminants may also originate from biochar [37]. Moreover, herbicides, e.g., atrazine and acetochlor, are sorbed on biochar [8], and this may reduce its efficacy [38] .

Furthermore, biochar has a remarkable effect on minimizing the emissions of greenhouse gases, especially CO2 [39, 40] vs. the traditional organic amendments [13]. Although biochar played important positive roles on sustaining the environment, there is a lake of knowledge concerning the recommended application rates of biochar to soils to avoid its negative potential impacts on the environment.

In this book, we will investigate the major techniques followed in the production and characterization of biochars. Their roles in sustaining agricultural productivity and environmental cleanup will be also a matter of concern. Finally, we will try to draw a legalization mode of biochar applications to the environment in order to ensure its safe applications.

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Acknowledgments

This study was supported by Shanghai Science and Technology Committee (Grant No. 29218230742600)-China.

References

  1. 1. Pariyar P et al. Evaluation of change in biochar properties derived from different feedstock and pyrolysis temperature for environmental and agricultural application. Science of the Total Environment. 2020;713:136433
  2. 2. Song X et al. Effect of cotton straw-derived materials on native soil organic carbon. Science of the Total Environment. 2019;663:38-44
  3. 3. Giagnoni L et al. Long-term soil biological fertility, volatile organic compounds and chemical properties in a vineyard soil after biochar amendment. Geoderma. 2019;344:127-136
  4. 4. Kätterer T et al. Biochar addition persistently increased soil fertility and yields in maize-soybean rotations over 10 years in sub-humid regions of Kenya. Field Crops Research. 2019;235:18-26
  5. 5. Awad YM et al. Chapter one - Biochar effects on rice paddy: Meta-analysis. In: Sparks DL, editor. Advances in Agronomy. Academic Press Inc. 2018. pp. 1-32
  6. 6. Leng L et al. Biochar stability assessment methods: A review. Science of the Total Environment. 2019;647:210-222
  7. 7. Abdelhafez AA, Abbas MHH, Li J. Biochar: The black diamond for soil sustainability, contamination control and agricultural production. In: Engineering Applications of Biochar. Rijeka: InTechOpen; 2017
  8. 8. Spokas KA et al. Impacts of woodchip biochar additions on greenhouse gas production and sorption/degradation of two herbicides in a Minnesota soil. Chemosphere. 2009;77(4):574-581
  9. 9. Elshony M et al. Ameliorating a Sandy soil using biochar and compost amendments and their implications as slow release fertilizers on plant growth. Egyptian Journal of Soil Science. 2019;59(4):305-322
  10. 10. Bassouny M, Abbas M. Role of biochar in managing the irrigation water requirements of maize plants: The pyramid model signifying the soil hydro-physical and environmental markers. Egyptian Journal of Soil Science. 2019;59(2):99-115
  11. 11. Fulton W et al. A simple technique to eliminate ethylene emissions from biochar amendment in agriculture. Agronomy for Sustainable Development. 2013;33(3):469-474
  12. 12. Spokas KA, Baker JM, Reicosky DC. Ethylene: Potential key for biochar amendment impacts. Plant and Soil. 2010;333:443-452
  13. 13. Rahman GKMM et al. Biochar and organic amendments for sustainable soil carbon and soil health. In: Datta R et al., editors. Carbon and Nitrogen Cycling in Soil. Singapore: Springer; 2020. pp. 45-85
  14. 14. Zheng H et al. Biochar-induced negative carbon mineralization priming effects in a coastal wetland soil: Roles of soil aggregation and microbial modulation. Science of the Total Environment. 2018;610-611:951-960
  15. 15. Wang J, Xiong Z, Kuzyakov Y. Biochar stability in soil: Meta-analysis of decomposition and priming effects. GCB Bioenergy. 2016;8(3):512-523
  16. 16. Kuzyakov Y, Bogomolova I, Glaser B. Biochar stability in soil: Decomposition during eight years and transformation as assessed by compound-specific 14C analysis. Soil Biology and Biochemistry. 2014;70:229-236
  17. 17. Williams H, Colombi T, Keller T. The influence of soil management on soil health: An on-farm study in southern Sweden. Geoderma. 2020;360:114010
  18. 18. Nakajima T. Soil health and carbon sequestration in urban farmland. In: Tojo S, editor. Recycle Based Organic Agriculture in a City. Singapore: Singapore: Springer; 2020. pp. 147-158
  19. 19. Sarfaraz Q et al. Characterization and carbon mineralization of biochars produced from different animal manures and plant residues. Scientific Reports. 2020;10(1):955
  20. 20. Abdelhafez AA, Li J, Abbas MHH. Feasibility of biochar manufactured from organic wastes on the stabilization of heavy metals in a metal smelter contaminated soil. Chemosphere. 2014;117:66-71
  21. 21. Dai Y et al. Utilization of biochar for the removal of nitrogen and phosphorus. Journal of Cleaner Production. 2020;257:120573
  22. 22. Prendergast-Miller MT, Duvall M, Sohi SP. Localisation of nitrate in the rhizosphere of biochar-amended soils. Soil Biology and Biochemistry. 2011;43(11):2243-2246
  23. 23. Manolikaki I, Diamadopoulos E. Agronomic potential of biochar prepared from brewery byproducts. Journal of Environmental Management. 2020;255:109856
  24. 24. Brassard P, Godbout S, Raghavan V. Soil biochar amendment as a climate change mitigation tool: Key parameters and mechanisms involved. Journal of Environmental Management. 2016;181:484-497
  25. 25. Werdin J et al. Biochar made from low density wood has greater plant available water than biochar made from high density wood. Science of the Total Environment. 2020;705:135856
  26. 26. Wiersma W et al. No effect of pyrolysis temperature and feedstock type on hydraulic properties of biochar and amended sandy soil. Geoderma. 2020;364:114209
  27. 27. Abel S et al. Impact of biochar and hydrochar addition on water retention and water repellency of sandy soil. Geoderma. 2013;202-203:183-191
  28. 28. Liu Z et al. Impacts of biochar concentration and particle size on hydraulic conductivity and DOC leaching of biochar–sand mixtures. Journal of Hydrology. 2016;533:461-472
  29. 29. Al-Wabel MI et al. Pyrolysis temperature induced changes in characteristics and chemical composition of biochar produced from conocarpus wastes. Bioresource Technology. 2013;131:374-379
  30. 30. Somerville PD et al. Biochar and compost equally improve urban soil physical and biological properties and tree growth, with no added benefit in combination. Science of the Total Environment. 2020;706:135736
  31. 31. Mukherjee A, Lal R. The biochar dilemma. Soil Research. 2014;52:217-230
  32. 32. Abdelhafez AA, Abbas MHH, Hamed MH. Biochar: A solution for soil Pb pollution. In: The 8th International Conference for Development and the Environment in the Arab World. Egypt: Assiut University; 2016. pp. 89-103
  33. 33. Weyers SL, Spokas KA. Impact of biochar on earthworm populations: A review. Applied and Environmental Soil Science. 2011;2011:541592
  34. 34. Thomas SC et al. Biochar mitigates negative effects of salt additions on two herbaceous plant species. Journal of Environmental Management. 2013;129:62-68
  35. 35. García-Jaramillo M et al. An examination of the role of biochar and biochar water-extractable substances on the sorption of ionizable herbicides in rice paddy soils. Science of the Total Environment. 2010;706:135682
  36. 36. Simiele M et al. Assisted phytoremediation of a former mine soil using biochar and iron sulphate: Effects on As soil immobilization and accumulation in three Salicaceae species. Science of the Total Environment. 2020;710:136203
  37. 37. Zhang C et al. Biochar for environmental management: Mitigating greenhouse gas emissions, contaminant treatment, and potential negative impacts. Chemical Engineering Journal. 2019;373:902-922
  38. 38. Graber ER et al. High surface area biochar negatively impacts herbicide efficacy. Plant and Soil. 2012;353:95-106
  39. 39. Puga AP et al. Biochar-based nitrogen fertilizers: Greenhouse gas emissions, use efficiency, and maize yield in tropical soils. Science of the Total Environment. 2020;704:135375
  40. 40. Wang H et al. Biochar mitigates greenhouse gas emissions from an acidic tea soil. Polish Journal of Environmental Studies. 2020;29:323-330

Written By

Ahmed A. Abdelhafez, Xu Zhang, Li Zhou, Guoyan Zou, Naxin Cui, Mohammed H.H. Abbas and Mahdy H. Hamed

Submitted: 06 January 2020 Published: 22 July 2020