Khan Bernine I, Solo-Gabriele Helena M, Dubey Brajesh K, Townsend Timothy G, Cai Yong
Department of Civil, Architectural, and Environmental Engineering, University of Miami, P.O. Box 248294, Coral Gables, Florida 33124-0630, USA.
Environ Sci Technol. 2004 Sep 1;38(17):4527-34. doi: 10.1021/es049598r.
For the past 60 yr, chromate-copper-arsenate (CCA) has been used to pressure-treat millions of cubic meters of wood in the United States for the construction of many outdoor structures. Leaching of arsenic from these structures is a possible health concern as there exists the potential for soil and groundwater contamination. While previous studies have focused on total arsenic concentrations leaching from CCA-treated wood, information pertaining to the speciation of arsenic leached is limited. Since arsenic toxicity is dependent upon speciation, the objective of this study was to identify and quantify arsenic species leaching from new and weathered CCA-treated wood and CCA-treated wood ash. Solvent-extraction experiments were carried out by subjecting the treated wood and the ash to solvents of varying pH values, solvents defined in the EPA's Synthetic Precipitation Leaching Procedure (SPLP) and Toxicity Characteristic Leaching Procedure (TCLP), rainwater, deionized water, and seawater. The generated leachates were analyzed for inorganic As(III) and As(V) and the organoarsenic species, monomethylarsonic acid (MMAA) and dimethylarsinic acid (DMAA), using high-performance liquid chromatography followed by hydride generation and atomic fluorescence spectrometry (HPLC-HG-AFS). Only the inorganic species were detected in any of the wood leachates; no organoarsenic species were found. Inorganic As(V) was the major detectable species leaching from both new and weathered wood. The weathered wood leached relatively more overall arsenic and was attributed to increased inorganic As(III) leaching. The greater presence of As(III) in the weathered wood samples as compared to the new wood samples may be due to natural chemical and biological transformations during the weathering process. CCA-treated wood ash leached more arsenic than unburned wood using the SPLP and TCLP, and ash samples leached more inorganic As(III) than the unburned counterparts. Increased leaching was due to higher concentrations of arsenic within the ash and to the conversion of some As(V) to As(III) during combustion.
在过去的60年里,铬酸铜砷酸盐(CCA)在美国被用于对数百万立方米的木材进行压力处理,以建造许多户外建筑结构。这些结构中砷的浸出可能会引发健康问题,因为存在土壤和地下水污染的潜在风险。虽然之前的研究主要关注从CCA处理过的木材中浸出的总砷浓度,但有关浸出砷形态的信息却很有限。由于砷的毒性取决于其形态,本研究的目的是识别和量化从新的和风化的CCA处理过的木材以及CCA处理过的木灰中浸出的砷形态。通过将处理过的木材和木灰置于不同pH值的溶剂(美国环境保护局的合成降雨浸出程序(SPLP)和毒性特性浸出程序(TCLP)中定义的溶剂)、雨水、去离子水和海水中,进行溶剂萃取实验。使用高效液相色谱法,随后进行氢化物发生和原子荧光光谱法(HPLC-HG-AFS),对生成的浸出液中的无机As(III)、As(V)以及有机砷形态一甲基胂酸(MMAA)和二甲基胂酸(DMAA)进行分析。在任何木材浸出液中仅检测到了无机形态;未发现有机砷形态。无机As(V)是从新的和风化木材中浸出的主要可检测形态。风化木材浸出的总砷相对较多,这归因于无机As(III)浸出的增加。与新木材样品相比,风化木材样品中As(III)的含量更高,这可能是由于风化过程中的自然化学和生物转化。使用SPLP和TCLP时,CCA处理过的木灰比未燃烧的木材浸出的砷更多,并且灰分样品浸出的无机As(III)比未燃烧的对应物更多。浸出增加是由于灰分中砷的浓度较高以及燃烧过程中一些As(V)转化为As(III)。