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Impact of Pyrolysis Temperature and Feedstock on Surface Charge and Functional Group Chemistry of Biochars
被引:142
作者:
Banik, Chumki
[1
]
Lawrinenko, Michael
[2
]
Bakshi, Santanu
[3
]
Laird, David A.
[1
]
机构:
[1] Iowa State Univ, Dept Agron, Ames, IA 50011 USA
[2] Actagro, Fresno, CA 93704 USA
[3] Connecticut Agr Expt Stn, Dept Environm Sci, New Haven, CT 06511 USA
基金:
美国食品与农业研究所;
关键词:
NUTRIENT RELEASE;
CARBON;
SOIL;
AMENDMENT;
WATER;
IMMOBILIZATION;
CONTAMINANTS;
NITROGEN;
SORPTION;
REMOVAL;
D O I:
10.2134/jeq2017.11.0432
中图分类号:
X [环境科学、安全科学];
学科分类号:
08 ;
0830 ;
摘要:
The capacity of biochars to adsorb ionic contaminants is strongly influenced by biochar surface chemistry. We studied the effects of biomass feedstock type, pyrolysis temperature, reaction media pH, and AlCl3 pre-pyrolysis feedstock treatments on biochar anion exchange capacity (AEC), cation exchange capacity (CEC), point of zero net charge (PZNC), and point of zero salt effect (PZSE). We used the relationship between PZNC and PZSE to probe biochar surfaces for the presence of unstable (hydrolyzable) surface charge functional groups. The results indicate that biochars produced at <= 500 degrees C have high CECs and low AEC, PZSE, and PZNC values due to the dominance of negative surface charge arising from carboxylate and phenolate functional groups. Biochars produced at >= 700 degrees C have low CEC and high AEC, PZSE, and PZNC values, consistent with a dominance of positive surface charge arising from nonhydrolyzable bridging oxonium (oxygen heterocycles) groups. However, biochars produced at moderate temperatures (500-700 degrees C) have high PZSE and low PZNC values, indicating the presence of nonbridging oxonium groups, which are rapidly degraded under alkaline conditions by OH- attack on the oxonium alpha-C. Biochars treated with AlCl3 have high AEC, PZSE, and PZNC values due to variably charged aluminol groups on biochar surfaces. The results provide support for the presence of both hydrolyzable and nonhydrolyzable oxonium groups on biochar surfaces. They also demonstrate that biochars produced at high pyrolysis temperatures (>700 degrees C) or those receiving pre-pyrolysis treatments with AlCl3 are optimized for anionic contaminant adsorption, whereas biochars produced at low pyrolysis temperatures (400 degrees C) are optimized for cationic contaminant adsorption.
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页码:452 / 461
页数:10
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