Cuypers Frederic, De Dobbelaere Christopher, Hardy An, Van Bael Marlies K, Helsen Lieve
Department of Mechanical Engineering, Division of Applied Mechanics and Energy Conversion, Katholieke Universiteit Leuven, Celestijnenlaan 300A, B-3001 Heverlee, Belgium.
J Hazard Mater. 2009 Jul 30;166(2-3):1238-43. doi: 10.1016/j.jhazmat.2008.12.048. Epub 2008 Dec 11.
The thermal stability and desorption of arsenic trioxide (As(2)O(3)) adsorbed on activated carbon (AC) was investigated as this phenomenon is expected to influence the arsenic release during low temperature pyrolysis of chromated copper arsenate (CCA) wood waste. Firstly, a thermogravimetric (TG) experiment with arsenolite, an allotropic form of As(2)O(3), was performed. The sample starts to sublime at temperatures lower than 200 degrees C with a sublimation peak temperature of 271 degrees C. Subsequently, TG experiments with samples of As(2)O(3) adsorbed on AC revealed that only very little (max. 6+/-3 wt%) As(2)O(3) was volatilized at temperatures below 280 degrees C, while still 41.6 (+/-5)wt% of the original arsenic concentration was retained at 440 degrees C and 28.5 (+/-3)wt% at 600 degrees C. The major arsenic volatilization occurred between 300 degrees C and 500 degrees C. The kinetic parameters of desorption, activation energy of desorption (E(d)) and pre-exponential factor (A), were determined by fitting an Arrhenius model to the experimental data, resulting in E(d)=69 kJ/mol, A=1.21 x 10(4)s(-1). It can be concluded that the adsorption of As(2)O(3) on AC can contribute to the thermal stabilisation of As(2)O(3). Consequently, during low temperature pyrolysis of CCA wood arsenic release may be prevented by adsorption of As(2)O(3) on the coal-type product formed during the thermal decomposition of the wood.
研究了吸附在活性炭(AC)上的三氧化二砷(As₂O₃)的热稳定性和解吸情况,因为预计这一现象会影响铬酸铜砷(CCA)木材废料低温热解过程中的砷释放。首先,对毒砂(As₂O₃的一种同质异形体)进行了热重(TG)实验。样品在低于200℃的温度下开始升华,升华峰值温度为271℃。随后,对吸附在AC上的As₂O₃样品进行的TG实验表明,在低于280℃的温度下,只有极少部分(最大6±3 wt%)的As₂O₃挥发,而在440℃时仍保留了41.6(±5)wt%的原始砷浓度,在600℃时为28.5(±3)wt%。主要的砷挥发发生在300℃至500℃之间。通过将Arrhenius模型拟合到实验数据中,确定了解吸的动力学参数,即解吸活化能(E(d))和指前因子(A),结果为E(d)=69 kJ/mol,A=1.21×10⁴ s⁻¹。可以得出结论,As₂O₃在AC上的吸附有助于As₂O₃的热稳定。因此,在CCA木材的低温热解过程中,As₂O₃在木材热分解过程中形成的煤型产物上的吸附可能会阻止砷的释放。