Although liquefaction technology has been extensively applied, plenty of biomass remains tainted with heavy metals (HMs). A meta-analysis of literature published from 2010 to 2023 was conducted to investigate the effects of liquefaction conditions and biomass characteristics on the remaining ratio and chemical speciation of HMs in biochar, aiming to achieve harmless treatment of biomass contaminated with HMs. The results showed that a liquefaction time of 1–3 h led to the largest HMs remaining ratio in biochar, with the mean ranging from 84.09% to 92.76%, compared with liquefaction times of less than 1 h and more than 3 h. Organic and acidic solvents liquefied biochar exhibited the greatest and lowest HMs remaining ratio. The effect of liquefaction temperature on HMs remaining ratio was not significant. The C, H, O, volatile matter, and fixed carbon contents of biomass were negatively correlated with the HMs remaining ratio, and N, S, and ash were positively correlated. In addition, liquefaction significantly transformed the HMs in biochar from bioavailable fractions (F1 and F2) to stable fractions (F3) (P < 0.05) when the temperature was increased to 280–330 ℃, with a liquefaction time of 1–3 h, and organic solvent as the liquefaction solvent. N and ash in biomass were positively correlated with the residue state (F4) of HMs in biochar and negatively correlated with F1 or F2, while H, O, fixed carbon, and volatile matter were negatively correlated with F4 but positively correlated with F3. Machine learning results showed that the contribution of biomass characteristics to HMs remaining ratio was higher than that of liquefaction factor. The most prominent contribution to the chemical speciation changes of HMs was the characteristics of HMs themselves, followed by ash content in biomass, liquefaction time, and C content. The findings of this meta-analysis contribute to factor selection, modification, and application of liquefied biomass to reducing risks.
Citation: Li Ma, Likun Zhan, Qingdan Wu, Longcheng Li, Xiaochen Zheng, Zhihua Xiao, Jingchen Zou. Optimization of liquefaction process based on global meta-analysis and machine learning approach: Effect of process conditions and raw material selection on remaining ratio and bioavailability of heavy metals in biochar[J]. AIMS Environmental Science, 2024, 11(3): 342-359. doi: 10.3934/environsci.2024016
Although liquefaction technology has been extensively applied, plenty of biomass remains tainted with heavy metals (HMs). A meta-analysis of literature published from 2010 to 2023 was conducted to investigate the effects of liquefaction conditions and biomass characteristics on the remaining ratio and chemical speciation of HMs in biochar, aiming to achieve harmless treatment of biomass contaminated with HMs. The results showed that a liquefaction time of 1–3 h led to the largest HMs remaining ratio in biochar, with the mean ranging from 84.09% to 92.76%, compared with liquefaction times of less than 1 h and more than 3 h. Organic and acidic solvents liquefied biochar exhibited the greatest and lowest HMs remaining ratio. The effect of liquefaction temperature on HMs remaining ratio was not significant. The C, H, O, volatile matter, and fixed carbon contents of biomass were negatively correlated with the HMs remaining ratio, and N, S, and ash were positively correlated. In addition, liquefaction significantly transformed the HMs in biochar from bioavailable fractions (F1 and F2) to stable fractions (F3) (P < 0.05) when the temperature was increased to 280–330 ℃, with a liquefaction time of 1–3 h, and organic solvent as the liquefaction solvent. N and ash in biomass were positively correlated with the residue state (F4) of HMs in biochar and negatively correlated with F1 or F2, while H, O, fixed carbon, and volatile matter were negatively correlated with F4 but positively correlated with F3. Machine learning results showed that the contribution of biomass characteristics to HMs remaining ratio was higher than that of liquefaction factor. The most prominent contribution to the chemical speciation changes of HMs was the characteristics of HMs themselves, followed by ash content in biomass, liquefaction time, and C content. The findings of this meta-analysis contribute to factor selection, modification, and application of liquefied biomass to reducing risks.
[1] | Wang X, Li C, Zhang B, et al. (2016) Migration and risk assessment of heavy metals in sewage sludge during hydrothermal treatment combined with pyrolysis. Bioresour Technol 221: 560–567. https://doi.org/10.1016/j.biortech.2016.09.069 doi: 10.1016/j.biortech.2016.09.069 |
[2] | Sharma HB, Sarmah AK, Dubey B (2020) Hydrothermal carbonization of renewable waste biomass for solid biofuel production: A discussion on process mechanism, the influence of process parameters, environmental performance and fuel properties of hydrochar. Renew Sust Energ Rev 123: 109761. https://doi.org/10.1016/j.rser.2020.109761 doi: 10.1016/j.rser.2020.109761 |
[3] | Castro JS, Assemany PP, Carneiro ACO, et al. (2021) Hydrothermal carbonization of microalgae biomass produced in agro-industrial effluent: Products, characterization and applications. Sci Total Environ 768: 144480. https://doi.org/10.1016/j.scitotenv.2020.144480 doi: 10.1016/j.scitotenv.2020.144480 |
[4] | Wang H, Yang Z, Li X, et al. (2020) Distribution and transformation behaviors of heavy metals and phosphorus during hydrothermal carbonization of sewage sludge. Environ Sci Pollut R 27: 17109–17122. https://doi.org/10.1007/s11356-020-08098-4 doi: 10.1007/s11356-020-08098-4 |
[5] | Wang JX, Chen SW, Lai FY, et al. (2020) Microwave-assisted hydrothermal carbonization of pig feces for the production of hydrochar. J Supercrit Fluid 162: 104858. https://doi.org/10.1016/j.supflu.2020.104858 doi: 10.1016/j.supflu.2020.104858 |
[6] | Tsai WT, Liu SC, Chen HR, et al. (2012) Textural and chemical properties of swine-manure-derived biochar pertinent to its potential use as a soil amendment. Chemosphere 89: 198–203. https://doi.org/10.1016/j.chemosphere.2012.05.085 doi: 10.1016/j.chemosphere.2012.05.085 |
[7] | Chen H, Wang X, Lu X, et al. (2018) Hydrothermal conversion of Cd-enriched rice straw and Cu-enriched Elsholtzia splendens with the aims of harmless treatment and resource reuse. Ind Eng Chem Res 57: 15683–15689. https://doi.org/10.1021/acs.iecr.8b04378 doi: 10.1021/acs.iecr.8b04378 |
[8] | Xu X, Wu Y, Wu X, et al. (2022) Effect of physicochemical properties of biochar from different feedstock on remediation of heavy metal contaminated soil in mining area. Surf Interfaces 32: 102058. https://doi.org/10.1016/j.surfin.2022.102058 doi: 10.1016/j.surfin.2022.102058 |
[9] | Celletti S, Bergamo A, Benedetti V, et al. (2021) Phytotoxicity of hydrochars obtained by hydrothermal carbonization of manure-based digestate. J Environ. Manage 280: 111635. https://doi.org/10.1016/j.jenvman.2020.111635 doi: 10.1016/j.jenvman.2020.111635 |
[10] | Zhang Y, Liu S, Niu L, et al. (2023) Sustained and efficient remediation of biochar immobilized with Sphingobium abikonense on phenanthrene-copper co-contaminated soil and microbial preferences of the bacteria colonized in biochar. Biochar 5. https://doi.org/10.1007/s42773-023-00241-x doi: 10.1007/s42773-023-00241-x |
[11] | Li X, Li R, Zhan M, et al. (2024) Combined magnetic biochar and ryegrass enhanced the remediation effect of soils contaminated with multiple heavy metals. Environ Int 185: 108498. https://doi.org/10.1016/j.envint.2024.108498 doi: 10.1016/j.envint.2024.108498 |
[12] | Li H, Yuan X, Zeng G, et al. (2010) The formation of bio-oil from sludge by deoxy-liquefaction in supercritical ethanol. Bioresource Technol 101: 2860–2866. https://doi: 10.1016/j.biortech.2009.10.084 doi: 10.1016/j.biortech.2009.10.084 |
[13] | Jiang H, Yan R, Cai C, et al. (2021) Hydrothermal liquefaction of Cd-enriched Amaranthus hypochondriacus L. in ethanol-water co-solvent: Focus on low-N bio-oil and heavy metal/metal-like distribution. Fuel 303: 121235. https://doi.org/10.1016/j.fuel.2021.121235 doi: 10.1016/j.fuel.2021.121235 |
[14] | Lee J, Park KY (2021) Conversion of heavy metal-containing biowaste from phytoremediation site to value-added solid fuel through hydrothermal carbonization. Environ Pollut 269: 116127. https://doi.org/10.1016/j.envpol.2020.116127 doi: 10.1016/j.envpol.2020.116127 |
[15] | Fang J, Gao B, Chen J, et al. (2015) Hydrochars derived from plant biomass under various conditions: Characterization and potential applications and impacts. Chem Eng J 267: 253–259. https://doi.org/10.1016/j.cej.2015.01.026 doi: 10.1016/j.cej.2015.01.026 |
[16] | Reza MT, Lynam JG, Uddin MH, et al. (2013) Hydrothermal carbonization: Fate of inorganics. Biomass Bioenergy 49: 86–94. https://doi.org/10.1016/j.biombioe.2012.12.004 doi: 10.1016/j.biombioe.2012.12.004 |
[17] | Lang Q, Guo Y, Zheng Q, et al. (2018) Co-hydrothermal carbonization of lignocellulosic biomass and swine manure: Hydrochar properties and heavy metal transformation behavior. Bioresource Technol 266: 242–248. https://doi.org/10.1016/j.biortech.2018.06.084 doi: 10.1016/j.biortech.2018.06.084 |
[18] | Fu H, Wang B, Wang H, et al. (2022) Assessment of livestock manure-derived hydrochar as cleaner products: Insights into basic properties, nutrient composition, and heavy metal content. J Clean Prod 330: 129820. https://doi.org/10.1016/j.jclepro.2021.129820 doi: 10.1016/j.jclepro.2021.129820 |
[19] | Ren J, Wang F, Zhai Y, et al. (2017) Effect of sewage sludge hydrochar on soil properties and Cd immobilization in a contaminated soil. Chemosphere 189: 627–633. https://doi.org/10.1016/j.chemosphere.2017.09.102 doi: 10.1016/j.chemosphere.2017.09.102 |
[20] | Peng N, Li Y, Liu T, et al. (2017) Polycyclic aromatic hydrocarbons and toxic heavy metals in municipal solid waste and corresponding hydrochars. Energ Fuel 31: 1665–1671. https://doi.org/10.1021/acs.energyfuels.6b02964 doi: 10.1021/acs.energyfuels.6b02964 |
[21] | Sun Y, Gao B, Yao Y, et al. (2014) Effects of feedstock type, production method, and pyrolysis temperature on biochar and hydrochar properties. Chem Eng J 240: 574–578. http://dx.doi.org/10.1016/j.cej.2013.10.081 doi: 10.1016/j.cej.2013.10.081 |
[22] | Zhou X, Zhao J, Chen M, et al. (2022) Influence of catalyst and solvent on the hydrothermal liquefaction of woody biomass. Bioresource Technol 346: 126354. https://doi.org/10.1016/j.biortech.2021.126354 doi: 10.1016/j.biortech.2021.126354 |
[23] | Hassan M, Liu Y, Naidu R, et al. (2020) Influences of feedstock sources and pyrolysis temperature on the properties of biochar and functionality as adsorbents: A meta-analysis. Sci Total Environ 744: 140714. https://doi.org/10.1016/j.scitotenv.2020.140714 doi: 10.1016/j.scitotenv.2020.140714 |
[24] | Li H, Lu J, Zhang Y, et al. (2018) Hydrothermal liquefaction of typical livestock manures in China: Biocrude oil production and migration of heavy metals. J Anal Appl Pyrol 135: 133–140. https://doi.org/10.1016/j.jaap.2018.09.010 doi: 10.1016/j.jaap.2018.09.010 |
[25] | Zhang J, Wang Y, Wang X, et al. (2022) Hydrothermal conversion of Cd/Zn hyperaccumulator (Sedum alfredii) for heavy metal separation and hydrochar production. J Hazard Mater 423: 127122. https://doi.org/10.1016/j.jhazmat.2021.127122 doi: 10.1016/j.jhazmat.2021.127122 |
[26] | Wang YJ, Yu Y, Huang HJ, et al. (2022) Efficient conversion of sewage sludge into hydrochar by microwave-assisted hydrothermal carbonization. Sci Total Environ 803: 149874. https://doi.org/10.1016/j.scitotenv.2021.149874 doi: 10.1016/j.scitotenv.2021.149874 |
[27] | Song C, Shan S, Muller K, et al. (2018) Characterization of pig manure-derived hydrochars for their potential application as fertilizer. Environ Sci Pollut R 25: 25772–25779. https://doi.org/10.1007/s11356-017-0301-y doi: 10.1007/s11356-017-0301-y |
[28] | Shafizadeh A, Shahbeig H, Nadian MH, et al. (2022) Machine learning predicts and optimizes hydrothermal liquefaction of biomass. Chem Eng J 445. https://doi.org/10.1016/j.cej.2022.136579 doi: 10.1016/j.cej.2022.136579 |
[29] | Luutu H, Rose MT, McIntosh S, et al. (2021) Plant growth responses to soil-applied hydrothermally-carbonised waste amendments: A meta-analysis. Plant Soil 472: 1–15. https://doi.org/10.1007/s11104-021-05185-4 doi: 10.1007/s11104-021-05185-4 |
[30] | Zhang S, Wei L, Trakal L, et al. (2024) Pyrolytic and hydrothermal carbonization affect the transformation of phosphorus fractions in the biochar and hydrochar derived from organic materials: A meta-analysis study. Sci Total Environ 906: 167418. https://doi.org/10.1016/j.scitotenv.2023.167418 doi: 10.1016/j.scitotenv.2023.167418 |
[31] | Lyu C, Li X, Yuan P, et al. (2021) Nitrogen retention effect of riparian zones in agricultural areas: A meta-analysis. J Clean Prod 315: 128143. https://doi.org/10.1016/j.jclepro.2021.128143 doi: 10.1016/j.jclepro.2021.128143 |
[32] | Sun G, Sun M, Du L, et al. (2021) Ecological rice-cropping systems mitigate global warming–A meta-analysis. Sci Total Environ 789: 147900. https://doi.org/10.1016/j.scitotenv.2021.147900 doi: 10.1016/j.scitotenv.2021.147900 |
[33] | Liu C, Bol R, Ju X, et al. (2023) Trade-offs on carbon and nitrogen availability lead to only a minor effect of elevated CO2 on potential denitrification in soil. Soil Biol Biochem 176: 108888. https://doi.org/10.1016/j.soilbio.2022.108888 doi: 10.1016/j.soilbio.2022.108888 |
[34] | Zeng X, Xiao Z, Zhang G, et al. (2018) Speciation and bioavailability of heavy metals in pyrolytic biochar of swine and goat manures. J Anal Appl Pyrol 132: 82–93. https://doi.org/10.1016/j.jaap.2018.03.012 doi: 10.1016/j.jaap.2018.03.012 |
[35] | Hu B, Xue J, Zhou Y, et al. (2020) Modelling bioaccumulation of heavy metals in soil-crop ecosystems and identifying its controlling factors using machine learning. Environ Pollut 262: 114308. https://doi.org/10.1016/j.envpol.2020.114308 doi: 10.1016/j.envpol.2020.114308 |
[36] | Tang Q, Chen Y, Yang H, et al. (2021) Machine learning prediction of pyrolytic gas yield and compositions with feature reduction methods: Effects of pyrolysis conditions and biomass characteristics. Bioresource Technol 339: 125581. https://doi.org/10.1016/j.biortech.2021.125581 doi: 10.1016/j.biortech.2021.125581 |
[37] | Li H, Wu Y, Liu S, et al. (2022) Decipher soil organic carbon dynamics and driving forces across China using machine learning. Global Change Biol 28: 3394–3410. https://doi.org/10.1111/gcb.16154 doi: 10.1111/gcb.16154 |
[38] | Selvam SM, Balasubramanian P (2022) Influence of biomass composition and microwave pyrolysis conditions on biochar yield and its properties: A machine learning approach. BioEnerg Res 16: 138–150. https://doi.org/10.1007/s12155-022-10447-9 doi: 10.1007/s12155-022-10447-9 |
[39] | Zhang W, Chen Q, Chen J, et al. (2023) Machine learning for hydrothermal treatment of biomass: A review. Bioresource Technol 370: 128547. https://doi.org/10.1016/j.biortech.2022.128547 doi: 10.1016/j.biortech.2022.128547 |
[40] | Chen Y, Dong L, Miao J, et al. (2019) Hydrothermal liquefaction of corn straw with mixed catalysts for the production of bio-oil and aromatic compounds. Bioresource Technol 294: 122148. https://doi.org/10.1016/j.biortech.2019.122148 doi: 10.1016/j.biortech.2019.122148 |
[41] | Chen H, Wang X, Lyu X, et al. (2019) Hydrothermal conversion of the hyperaccumulator Sedum alfredii Hance for efficiently recovering heavy metals and bio-oil. J Environ Chem Eng 7. https://doi.org/10.1016/j.jece.2019.103321 doi: 10.1016/j.jece.2019.103321 |
[42] | Chi T, Zuo J, Liu F (2017) Performance and mechanism for cadmium and lead adsorption from water and soil by corn straw biochar. Front Env Sci Eng 11. https://doi.org/10.1007/s11783-017-0921-y doi: 10.1007/s11783-017-0921-y |
[43] | He C, Zhang Z, Xie C, et al. (2021) Transformation behaviors and environmental risk assessment of heavy metals during resource recovery from Sedum plumbizincicola via hydrothermal liquefaction. J Hazard Mater 410: 124588. https://doi.org/10.1016/j.jhazmat.2020.124588 doi: 10.1016/j.jhazmat.2020.124588 |
[44] | Lu J, Watson J, Zeng J, et al. (2018) Biocrude production and heavy metal migration during hydrothermal liquefaction of swine manure. Process Saf Environ 115: 108–115. https://doi.org/10.1016/j.psep.2017.11.001 doi: 10.1016/j.psep.2017.11.001 |
[45] | Chen H, Zhai Y, Xu B, et al. (2014) Fate and risk assessment of heavy metals in residue from co-liquefaction of Camellia oleifera cake and sewage sludge in supercritical ethanol. Bioresource Technol 167: 578–581. https://doi.org/10.1016/j.biortech.2014.06.048 doi: 10.1016/j.biortech.2014.06.048 |
[46] | Xiao XF, Chang YC, Lai FY, et al. (2020) Effects of rice straw/wood sawdust addition on the transport/conversion behaviors of heavy metals during the liquefaction of sewage sludge. J Environ Manage 270: 110824. https://doi.org/10.1016/j.jenvman.2020.110824 doi: 10.1016/j.jenvman.2020.110824 |
[47] | Xiao Z, Yuan X, Jiang L, et al. (2015) Energy recovery and secondary pollutant emission from the combustion of co-pelletized fuel from municipal sewage sludge and wood sawdust. Energy 91: 441–450. https://doi.org/10.1016/j.energy.2015.08.077 doi: 10.1016/j.energy.2015.08.077 |
[48] | Wang L, Chang Y, Liu Q (2019) Fate and distribution of nutrients and heavy metals during hydrothermal carbonization of sewage sludge with implication to land application. J Clean Prod 225: 972–983. https://doi.org/10.1016/j.jclepro.2019.03.347 doi: 10.1016/j.jclepro.2019.03.347 |
[49] | Alipour M, Asadi H, Chen C, et al. (2021) Bioavailability and eco-toxicity of heavy metals in chars produced from municipal sewage sludge decreased during pyrolysis and hydrothermal carbonization. Ecol Eng 162. https://doi.org/10.1016/j.ecoleng.2021.106173 doi: 10.1016/j.ecoleng.2021.106173 |
[50] | Shao J, Yuan X, Leng L, et al. (2015) The comparison of the migration and transformation behavior of heavy metals during pyrolysis and liquefaction of municipal sewage sludge, paper mill sludge, and slaughterhouse sludge. Bioresource Technol 198: 16–22. https://doi.org/10.1016/j.biortech.2015.08.147 doi: 10.1016/j.biortech.2015.08.147 |
[51] | Wei S, Zhu M, Fan X, et al. (2019) Influence of pyrolysis temperature and feedstock on carbon fractions of biochar produced from pyrolysis of rice straw, pine wood, pig manure and sewage sludge. Chemosphere 218: 624–631. https://doi.org/10.1016/j.chemosphere.2018.11.177 doi: 10.1016/j.chemosphere.2018.11.177 |
[52] | Huang HJ, Yuan XZ (2016) The migration and transformation behaviors of heavy metals during the hydrothermal treatment of sewage sludge. Bioresource Technol 200: 991–998. https://doi.org/10.1016/j.biortech.2015.10.099 doi: 10.1016/j.biortech.2015.10.099 |
[53] | Yuan X, Leng L, Huang H, et al. (2015) Speciation and environmental risk assessment of heavy metal in bio-oil from liquefaction/pyrolysis of sewage sludge. Chemosphere 120: 645–652. https://doi.org/10.1016/j.chemosphere.2014.10.010 doi: 10.1016/j.chemosphere.2014.10.010 |
[54] | Chen S, Chen L, Wang D, et al. (2022) Low pe+pH induces inhibition of cadmium sulfide precipitation by methanogenesis in paddy soil. J Hazard Mater 437: 129297. https://doi.org/10.1016/j.jhazmat.2022.129297 doi: 10.1016/j.jhazmat.2022.129297 |
[55] | Sun FS, Yu GH, Ning JY, et al. (2020) Biological removal of cadmium from biogas residues during vermicomposting, and the effect of earthworm hydrolysates on Trichoderma guizhouense sporulation. Bioresource Technol 312: 123635. https://doi.org/10.1016/j.biortech.2020.123635 doi: 10.1016/j.biortech.2020.123635 |
[56] | Sun FS, Yu GH, Polizzotto ML, et al. (2019) Toward understanding the binding of Zn in soils by two-dimensional correlation spectroscopy and synchrotron-radiation-based spectromicroscopies. Geoderma 337: 238–245. https://doi.org/10.1016/j.geoderma.2018.09.032 doi: 10.1016/j.geoderma.2018.09.032 |