Toxic and nontoxic elemental enrichment in biochar at different production temperatures

被引:16
作者
Anyika, Chinedum [1 ]
Majid, Zaiton Abdul [2 ]
Rashid, Moh'd [4 ]
Isa, Abdullahi Bala [6 ]
Ismail, Norzubaidha [5 ]
Zakaria, Mohamad Pauzi [3 ]
Yahya, Adibah [1 ]
机构
[1] Univ Teknol Malaysia, Fac Biosci & Med Engn, Johor Baharu 81310, Malaysia
[2] Univ Teknol Malaysia, Dept Chem, Fac Sci, Johor Baharu 81310, Malaysia
[3] Univ Malaya, IOES, Bachok Marine Res Stn, Bachok 16310, Kelantan, Malaysia
[4] Univ Teknol, Dept Environm Engn & Green Technol, MJIIT, Kuala Lumpur, Malaysia
[5] Univ Teknol Malaysia, Univ Ind Res Lab, Johor Baharu 81310, Malaysia
[6] Fed Univ Technol, Adv Off, Minna, Nigeria
关键词
Toxic and nontoxic elements; Enrichment; ICP-OES; MA 3000 Mercury Analyser; Biochar quality; Soil health; POLYCYCLIC AROMATIC-HYDROCARBONS; CCB-TREATED WOOD; WASTE-WATER; ACTIVATED CARBON; PYROLYSIS TEMPERATURE; AQUEOUS-SOLUTION; SLOW PYROLYSIS; BLACK CARBON; REMOVAL; METAL;
D O I
10.1016/j.jclepro.2016.04.043
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
The major impediment to the use of biochar for soil amendment is the presence of toxic elements; however, it is not known how variations in production temperature affect the enrichment behaviour of toxic elements as identified by mass loss and whether the level of nontoxic elements compromises biochar quality. These goals require an understanding of the solid phase which constitutes the tar and ash fractions that harbour majority of the Cation exchange capacity (CEC) and functional groups of biochars and the possible mechanisms through which these metals interact with the solid phase. Results showed that the enrichment behaviour of individual toxic and nontoxic elements at low production temperatures of 350 and 450 was significantly different (p < 0.005) to that of high production temperature of 650 degrees C. The concentration of individual toxic elements revealed maximum enrichment of 193,957 +/- 36,881 mu g kg(-1) and 1650 +/- 203 mu g kg(-1) for Na and B respectively at the 450 degrees C. While the concentrations of individual nontoxic elements, exhibited maximum enrichment of 665,187 +/- 119,715 mu g kg(-1), 58,335 +/- 13,985 mu g kg(-1), 8858 +/- 3574 mu g kg(-1) and 4907 +/- 1174 mu g kg(-1) for K, Mg, Si and Al respectively at the 450 degrees C. Conversely, As was the only toxic element that exhibited maximum enrichment of 21 +/- 9 mu g kg(-1), at the 650 degrees C. Total toxic elemental concentrations indicated strong relationship with percentage mass loss (r(2) = 0.998, p < 0.05), which.was greatest at 450 degrees C, but indicated strong negative relationship with percentage ash content (r(2) = 0.946, p < 0.210), which was greatest at 650 degrees C. Therefore, the 650 degrees C was effective in reducing both the toxic and nontoxic elements in biochar and thus, presented a quality biochar, due to its pi electrons which can result in dual benefits such as stronger binding of inorganic and organic elements to biochar in soils. (C) 2016 Elsevier Ltd. All rights reserved.
引用
收藏
页码:810 / 821
页数:12
相关论文
共 84 条
[51]   Dynamic Molecular Structure of Plant Biomass-Derived Black Carbon (Biochar) [J].
Keiluweit, Marco ;
Nico, Peter S. ;
Johnson, Mark G. ;
Kleber, Markus .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 2010, 44 (04) :1247-1253
[52]   Multi-walled carbon nanotubes-ionic liquid-carbon paste electrode as a super selectivity sensor: Application to potentiometric monitoring of mercury ion(II) [J].
Khani, Hadi ;
Rofouei, Mohammad Kazem ;
Arab, Pezhman ;
Gupta, Vinod Kumar ;
Vafaei, Zahra .
JOURNAL OF HAZARDOUS MATERIALS, 2010, 183 (1-3) :402-409
[53]   Characterization of pyrolytic products obtained from fast pyrolysis of chromated copper arsenate (CCA)- and alkaline copper quaternary compounds (ACQ)-treated wood biomasses [J].
Kim, Jae-Young ;
Kim, Tae-Sung ;
Eom, In-Yong ;
Kang, Sung Mo ;
Cho, Tae-Su ;
Choi, In Gyu ;
Choi, Joon Weon .
JOURNAL OF HAZARDOUS MATERIALS, 2012, 227 :445-452
[54]   Slow pyrolysis of CCB-treated wood for energy recovery: Influence of chromium, copper and boron on pyrolysis process and optimization [J].
Kinata, Silao Esperance ;
Loubar, Khaled ;
Pataschiv, Maria ;
Bouslamti, Amine ;
Belloncle, Christophe ;
Tazerout, Mohand .
JOURNAL OF ANALYTICAL AND APPLIED PYROLYSIS, 2013, 104 :210-217
[55]   Influence of impregnation method on metal retention of CCB-treated wood in slow pyrolysis process [J].
Kinata, Silao Esperance ;
Loubar, Khaled ;
Bouslamti, Amine ;
Belloncle, Christophe ;
Tazerout, Mohand .
JOURNAL OF HAZARDOUS MATERIALS, 2012, 233 :172-176
[56]   How does fire affect the nature and stability of soil organic nitrogen and carbon? A review [J].
Knicker, Heike .
BIOGEOCHEMISTRY, 2007, 85 (01) :91-118
[57]   Thermoanalytical investigation of lignite humic acids fractions [J].
Kucerík, J ;
Kovár, J ;
Pekar, M .
JOURNAL OF THERMAL ANALYSIS AND CALORIMETRY, 2004, 76 (01) :55-65
[58]  
Lehmann J., 2009, BIOCHAR ENV MANAGEME, P1
[59]  
Lehmann J., 2009, EARTHSCAN
[60]   TRACE-METAL TRANSFORMATION MECHANISMS DURING COAL COMBUSTION [J].
LINAK, WP ;
WENDT, JOL .
FUEL PROCESSING TECHNOLOGY, 1994, 39 (1-3) :173-198