Jung Hun-Bok, Yun Seong-Taek, Kim Soon-Oh, Jung Myung Chae, So Chil-Sup, Koh Yong-Kwon
Department of Earth and Environmental Sciences, Korea University, 136-701, Seoul, Republic of Korea.
Environ Geochem Health. 2006 Jun;28(3):283-96. doi: 10.1007/s10653-006-9044-2. Epub 2006 Apr 29.
We assessed the use of anodic stripping voltammetry (ASV) for in-situ determinations of both total concentration and speciation of dissolved heavy metals (Cd, Cu, Pb and Zn) in acid mine drainage (AMD). In the Kwangyang Au-Ag mine area of South Korea, different sites with varying water chemistry within an AMD were studied with a field portable anodic stripping voltammeter. Anodic stripping voltammetry after wet oxidation (acidification) was very sensitive enough to determine total concentration of dissolved Cd because Cd was dominantly present as 'labile' species, whilst the technique was not so effective for determining total Cu especially in the downstream sites from the retention pond, due to its complexation with organic matter. For dissolved Pb, the concentrations determined by ASV after wet oxidation generally agreed with those by ICP-AES. In the downstream samples (pH>5), however, ASV data after wet oxidation were lower than ICP-AES data because a significant fraction of dissolved Pb was present in those samples as 'inert' species associated with colloidal iron oxide particles. The determination of total dissolved Zn by ASV after wet oxidation appeared to be unsatisfactory for the samples with high Cu content, possibly due to the interference by the formation of Zn-Cu intermetallic compounds on the mercury coated electrode. In AMD samples with high dissolved iron, use of ultraviolet irradiation was not effective for determining total concentrations because humate destruction by UV irradiation possibly resulted in the removal of a part of dissolved heavy metals from waters through the precipitation of iron hydroxides.
我们评估了阳极溶出伏安法(ASV)用于原位测定酸性矿山排水(AMD)中溶解态重金属(镉、铜、铅和锌)的总浓度及形态。在韩国光阳金 - 银矿区,使用现场便携式阳极溶出伏安仪对AMD内不同水化学性质的位点进行了研究。湿氧化(酸化)后的阳极溶出伏安法对于测定溶解态镉的总浓度非常灵敏,因为镉主要以“不稳定”形态存在,而该技术对于测定总铜尤其是在滞留池下游位点不太有效,这是由于铜与有机物发生了络合作用。对于溶解态铅,湿氧化后通过ASV测定的浓度一般与电感耦合等离子体原子发射光谱法(ICP - AES)测定的值一致。然而,在下游样品(pH>5)中,湿氧化后的ASV数据低于ICP - AES数据,因为这些样品中相当一部分溶解态铅以与胶体氧化铁颗粒相关的“惰性”形态存在。对于高铜含量的样品,湿氧化后通过ASV测定总溶解态锌似乎并不令人满意,这可能是由于在汞膜电极上形成锌 - 铜金属间化合物产生了干扰。在溶解铁含量高的AMD样品中,使用紫外线照射对于测定总浓度并不有效,因为紫外线照射破坏腐殖酸盐可能导致一部分溶解态重金属通过氢氧化铁沉淀从水中去除。