Janos P, Fedorovic J, Stanková P, Grötschelová S, Rejnek J, Stopka P
Faculty of the Environment, University of Jan Evangelista Purkyne, Králova Výsina 7, 400 96 Ustí nad Labem, Czech Republic.
Environ Technol. 2006 Feb;27(2):169-81. doi: 10.1080/09593332708618627.
Iron humate produced as a waste by-product during an industrial manufacture of humic substances from low-rank brown coals was tested as a sorbent for the removal of metal cations--Cd (II), Cu (II), Co (II), Ni (II), Zn (II), TI (I), Eu (III), Cr (III)--as well as hexavalent chromium from waters. The Langmuir-type isotherms were used to describe the metal sorption; the respective equations may be derived and interpreted on the basis of a concept of surface-complexation reactions. Parameters of the sorption isotherms were estimated from experimental dependencies measured in a batch arrangement. The sorption capacities ranged from 0.024 mmol g(-1)for Co (II) to 0.324 mmol g(-1)for Tl(I). The metal uptake was affected by the presence of complexing agents (EDTA, salicylate, citrate), but this effect depends strongly on pH and the kind of complexing agent. The sorption of Cu (II) ions was suppressed in the presence of EDTA in an almost whole examined pH range (ca. 1-6.5) and in the presence of citrate at higher pH values (above pH 4). In the presence of salicylate, on the other hand, a slight sorption enhancement was observed. The metal sorption was suppressed also in the presence of anionic surfactant (sodium dodecylsulfate). Both in the presence as well as in the absence of complexing agents, the metal sorption showed a strong dependence on pH--the sorption was reduced considerably at low pH values below ca. 2. A typical working range for iron humate as a sorbent is ca. pH 3-5, where it exhibits a high buffering capacity, a sufficient stability and metal-binding capability.
在由低阶褐煤工业生产腐殖物质过程中产生的作为废弃物副产物的铁腐殖酸盐,被测试作为一种吸附剂用于去除水中的金属阳离子——镉(II)、铜(II)、钴(II)、镍(II)、锌(II)、铊(I)、铕(III)、铬(III)——以及六价铬。采用朗缪尔型等温线来描述金属吸附;相应的方程可基于表面络合反应的概念推导和解释。吸附等温线的参数由在分批实验装置中测量的实验相关性估算得出。吸附容量范围从钴(II)的0.024 mmol g⁻¹到铊(I)的0.324 mmol g⁻¹。金属的摄取受到络合剂(乙二胺四乙酸、水杨酸盐、柠檬酸盐)的影响,但这种影响强烈依赖于pH值和络合剂的种类。在几乎整个检测的pH范围(约1 - 6.5)内,乙二胺四乙酸存在时铜(II)离子的吸附受到抑制,在较高pH值(高于pH 4)时柠檬酸盐存在时也受到抑制。另一方面,水杨酸盐存在时观察到轻微的吸附增强。阴离子表面活性剂(十二烷基硫酸钠)存在时金属吸附也受到抑制。无论络合剂存在与否,金属吸附都强烈依赖于pH值——在低于约2的低pH值下吸附显著降低。铁腐殖酸盐作为吸附剂的典型工作范围约为pH 3 - 5,在此范围内它表现出高缓冲容量、足够的稳定性和金属结合能力。