Korea University, Seoul, Korea.
Environ Geochem Health. 2011 Jan;33 Suppl 1:81-9. doi: 10.1007/s10653-010-9357-z. Epub 2010 Nov 3.
This study examines the adsorption isotherms, kinetics and mechanisms of Pb²(+) sorption onto waste cow bone powder (WCBP) surfaces. The concentrations of Pb²(+) in the study range from 10 to 90 mg/L. Although the sorption data follow the Langmuir and Freundlich isotherm, a detailed examination reveals that surface sorption or complexation and co-precipitation are the most important mechanisms, along with possibly ion exchange and solid diffusion also contributing to the overall sorption process. The co-precipitation of Pb²(+) with the calcium hydroxyapatite (Ca-HAP) is implied by significant changes in Ca²(+) and PO₄³⁻ concentrations during the metal sorption processes. The Pb²(+) sorption onto the WCBP surface by metal complexation with surface functional groups such as ≡ POH. The major metal surface species are likely to be ≡ POPb(+). The sorption isotherm results indicated that Pb²(+) sorption onto the Langmuir and Freundlich constant q(max) and K( F ) is 9.52 and 8.18 mg g⁻¹, respectively. Sorption kinetics results indicated that Pb²(+) sorption onto WCBP was pseudo-second-order rate constants K₂ was 1.12 g mg⁻¹ h⁻¹. The main mechanism is adsorption or surface complexation (≡POPb(+): 61.6%), co-precipitation or ion exchange [Ca₃(.)₉₃ Pb₁(.)₀₇ (PO₄)₃ (OH): 21.4%] and other precipitation [Pb 50 mg L⁻¹ and natural pH: 17%). Sorption isotherms showed that WCBP has a much higher Pb²(+) removal rate in an aqueous solution; the greater capability of WCBP to remove aqueous Pb²(+) indicates its potential as another promising way to remediate Pb²(+)-contaminated media.
本研究考察了 Pb²(+)在废牛骨粉(WCBP)表面的吸附等温线、动力学和机制。研究中 Pb²(+)的浓度范围为 10-90mg/L。尽管吸附数据符合朗缪尔和弗雷德里希等温线,但详细研究表明,表面吸附或络合和共沉淀是最重要的机制,同时可能还有离子交换和固体扩散也对整个吸附过程有贡献。在金属吸附过程中,Ca²(+)和 PO₄³⁻浓度的显著变化表明 Pb²(+)与钙羟基磷灰石(Ca-HAP)共沉淀。Pb²(+)通过与表面官能团如≡POH 的金属络合作用吸附到 WCBP 表面。主要的金属表面物种可能是≡POPb(+)。吸附等温线结果表明,Pb²(+)在 Langmuir 和 Freundlich 常数 q(max)和 K( F )上的吸附分别为 9.52 和 8.18mg g⁻¹。吸附动力学结果表明,Pb²(+)在 WCBP 上的吸附符合准二级动力学速率常数 K₂为 1.12g mg⁻¹ h⁻¹。主要机制是吸附或表面络合(≡POPb(+):61.6%)、共沉淀或离子交换[Ca₃(.)₉₃Pb₁(.)₀₇(PO₄)₃(OH):21.4%]和其他沉淀[Pb 50mg L⁻¹和自然 pH:17%]。吸附等温线表明,WCBP 在水溶液中有更高的 Pb²(+)去除率;WCBP 去除水溶液中 Pb²(+)的能力更强,表明其作为另一种有前途的修复 Pb²(+)-污染介质的方法具有潜力。