农业环境科学学报
農業環境科學學報
농업배경과학학보
Journal of Agro-Environment Science
2014年
5期
958-964
,共7页
徐楠楠%林大松%徐应明%谢忠雷%梁学峰%郭文娟
徐楠楠%林大鬆%徐應明%謝忠雷%樑學峰%郭文娟
서남남%림대송%서응명%사충뢰%량학봉%곽문연
生物炭%镉%吸附%吸附动力学%影响因素
生物炭%鎘%吸附%吸附動力學%影響因素
생물탄%력%흡부%흡부동역학%영향인소
biochar%aquatic Cd2+%adsorption%adsorption characteristics%influencing factors
以玉米秸秆生物炭为实验材料,研究了生物炭吸附重金属Cd2+的性能,分析了吸附温度、吸附时间、初始pH值以及生物炭粒径对吸附的影响,并对吸附前后生物炭样品进行傅里叶变换红外光谱分析(FITR)、X-射线衍射(XRD)和X-射线光电子能谱(XPS)表征以分析吸附机理。结果表明:玉米秸秆生物炭对Cd2+的吸附可用Langmuir等温方程较好地拟合,在不同温度下其饱和吸附量分别为18.49 mg·g-1(288.15 K)、23.51 mg·g-1(298.15 K)、23.59 mg·g-1(308.15 K)和24.43 mg·g-1(318.15 K),吸附动力学过程可以由准二级动力学方程很好地拟合,约40 min即达平衡,pH值为5时吸附量最大,生物炭粒径对吸附无明显影响。结构表征表明,生物炭对Cd2+的吸附机理主要为表面羟基(-C-OH)和羰基(-C=O)与Cd2+发生络合化学反应作用。
以玉米秸稈生物炭為實驗材料,研究瞭生物炭吸附重金屬Cd2+的性能,分析瞭吸附溫度、吸附時間、初始pH值以及生物炭粒徑對吸附的影響,併對吸附前後生物炭樣品進行傅裏葉變換紅外光譜分析(FITR)、X-射線衍射(XRD)和X-射線光電子能譜(XPS)錶徵以分析吸附機理。結果錶明:玉米秸稈生物炭對Cd2+的吸附可用Langmuir等溫方程較好地擬閤,在不同溫度下其飽和吸附量分彆為18.49 mg·g-1(288.15 K)、23.51 mg·g-1(298.15 K)、23.59 mg·g-1(308.15 K)和24.43 mg·g-1(318.15 K),吸附動力學過程可以由準二級動力學方程很好地擬閤,約40 min即達平衡,pH值為5時吸附量最大,生物炭粒徑對吸附無明顯影響。結構錶徵錶明,生物炭對Cd2+的吸附機理主要為錶麵羥基(-C-OH)和羰基(-C=O)與Cd2+髮生絡閤化學反應作用。
이옥미갈간생물탄위실험재료,연구료생물탄흡부중금속Cd2+적성능,분석료흡부온도、흡부시간、초시pH치이급생물탄립경대흡부적영향,병대흡부전후생물탄양품진행부리협변환홍외광보분석(FITR)、X-사선연사(XRD)화X-사선광전자능보(XPS)표정이분석흡부궤리。결과표명:옥미갈간생물탄대Cd2+적흡부가용Langmuir등온방정교호지의합,재불동온도하기포화흡부량분별위18.49 mg·g-1(288.15 K)、23.51 mg·g-1(298.15 K)、23.59 mg·g-1(308.15 K)화24.43 mg·g-1(318.15 K),흡부동역학과정가이유준이급동역학방정흔호지의합,약40 min즉체평형,pH치위5시흡부량최대,생물탄립경대흡부무명현영향。결구표정표명,생물탄대Cd2+적흡부궤리주요위표면간기(-C-OH)화탄기(-C=O)여Cd2+발생락합화학반응작용。
Biochar has large surface and may be used to adsorb heavy metals from water. A lab experiment was carried out to investigate the effects of time, temperature(288.15~318.15 K), solution pH, and biochar particle size on adsorption of aquatic Cd2+by biochar. The surface characteristics of biochar before and after Cd2+adsorption were examined using X-ray diffraction analysis(XRD), Fourier transform infrared spectroscopy(FTIR)and X-ray Photoelectron Spectroscopy(XPS). The results showed that the equilibrium adsorption was better fit by Langmuir model than Freundlich model. The maximum adsorption capacity of the biochar for Cd2+at different temperatures was 18.49 mg·g-1 (288.15 K), 23.51 mg·g-1(298.15 K), 23.59 mg·g-1(308.15 K)and 24.43 mg·g-1(318.15 K), respectively. The adsorption kinetics could be well described by pseudo-second order kinetics model. The adsorption process was quick and the equilibrium was attained within 40 minutes. The optimum adsorption pH value was 5.0. The particle size of biochar had no significant effects on Cd2+adsorption. The biochar adsorbed Cd2+mainly via Cd2+chelation with hydroxyl(-C-OH)and carbonyl(-C=O)as confirmed by XRD, FTIR and XPS.