Zhu Yinian, Huang Bin, Zhu Zongqiang, Liu Huili, Huang Yanhua, Zhao Xin, Liang Meina
College of Environmental Science and Engineering, Guilin University of Technology, Guilin, 541004 People's Republic of China.
College of Light Industry and Food Engineering, Guangxi University, Nanning, 530004 People's Republic of China.
Geochem Trans. 2016 May 6;17:2. doi: 10.1186/s12932-016-0034-8. eCollection 2016.
The interaction between Ca-HAP and Pb(2+) solution can result in the formation of a hydroxyapatite-hydroxypyromorphite solid solution [(PbxCa1-x)5(PO4)3(OH)], which can greatly affect the transport and distribution of toxic Pb in water, rock and soil. Therefore, it's necessary to know the physicochemical properties of (PbxCa1-x)5(PO4)3(OH), predominantly its thermodynamic solubility and stability in aqueous solution. Nevertheless, no experiment on the dissolution and related thermodynamic data has been reported.
Dissolution of the hydroxypyromorphite-hydroxyapatite solid solution [(PbxCa1-x)5(PO4)3(OH)] in aqueous solution at 25 °C was experimentally studied. The aqueous concentrations were greatly affected by the Pb/(Pb + Ca) molar ratios (XPb) of the solids. For the solids with high XPb [(Pb0.89Ca0.11)5(PO4)3OH], the aqueous Pb(2+) concentrations increased rapidly with time and reached a peak value after 240-720 h dissolution, and then decreased gradually and reached a stable state after 5040 h dissolution. For the solids with low XPb (0.00-0.80), the aqueous Pb(2+) concentrations increased quickly with time and reached a peak value after 1-12 h dissolution, and then decreased gradually and attained a stable state after 720-2160 h dissolution.
The dissolution process of the solids with high XPb (0.89-1.00) was different from that of the solids with low XPb (0.00-0.80). The average K sp values were estimated to be 10(-80.77±0.20) (10(-80.57)-10(-80.96)) for hydroxypyromorphite [Pb5(PO4)3OH] and 10(-58.38±0.07) (10(-58.31)-10(-58.46)) for calcium hydroxyapatite [Ca5(PO4)3OH]. The Gibbs free energies of formation (ΔG f (o) ) were determined to be -3796.71 and -6314.63 kJ/mol, respectively. The solubility decreased with the increasing Pb/(Pb + Ca) molar ratios (XPb) of (PbxCa1‒x)5(PO4)3(OH). For the dissolution at 25 °C with an initial pH of 2.00, the experimental data plotted on the Lippmann diagram showed that the solid solution (PbxCa1-x)5(PO4)3(OH) dissolved stoichiometrically at the early stage of dissolution and moved gradually up to the Lippmann solutus curve and the saturation curve for Pb5(PO4)3OH, and then the data points moved along the Lippmann solutus curve from right to left. The Pb-rich (PbxCa1-x)5(PO4)3(OH) was in equilibrium with the Ca-rich aqueous solution. Graphical abstractLippmann diagrams for dissolution of the hydroxypyromorphite-hydroxyapatite solid solution [(PbxCa1-x)5(PO4)3OH] at 25 ˚C and an initial pH of 2.00.
钙羟基磷灰石(Ca-HAP)与Pb(2+)溶液之间的相互作用可导致形成羟基磷灰石-羟基氯磷灰石固溶体[(PbxCa1-x)5(PO4)3(OH)],这会极大地影响有毒铅在水、岩石和土壤中的迁移和分布。因此,有必要了解(PbxCa1-x)5(PO4)3(OH)的物理化学性质,主要是其在水溶液中的热力学溶解度和稳定性。然而,尚未有关于其溶解及相关热力学数据的实验报道。
对羟基氯磷灰石-羟基磷灰石固溶体[(PbxCa1-x)5(PO4)3(OH)]在25℃水溶液中的溶解进行了实验研究。水溶液浓度受固体中Pb/(Pb + Ca)摩尔比(XPb)的极大影响。对于高XPb的固体[(Pb0.89Ca0.11)5(PO4)3OH],水溶液中Pb(2+)浓度随时间迅速增加,在溶解240 - 720小时后达到峰值,然后逐渐降低,在溶解5040小时后达到稳定状态。对于低XPb(0.00 - 0.80)的固体,水溶液中Pb(2+)浓度随时间快速增加,在溶解1 - 12小时后达到峰值,然后逐渐降低,在溶解720 - 2160小时后达到稳定状态。
高XPb(0.89 - 1.00)的固体溶解过程与低XPb(0.00 - 0.80)的固体不同。羟基氯磷灰石[Pb5(PO4)3OH]的平均溶度积常数(Ksp)估计为10^(-80.77±0.20)(10^(-80.57) - 10^(-80.96)),羟基磷灰石[Ca5(PO4)3OH]的平均溶度积常数估计为10^(-58.38±0.07)(10^(-58.31) - 10^(-58.46))。生成吉布斯自由能(ΔGf(o))分别确定为-3796.71和-6314.63 kJ/mol。(PbxCa1‒x)5(PO4)3(OH)的溶解度随Pb/(Pb + Ca)摩尔比(XPb)的增加而降低。对于在25℃、初始pH为2.00的溶解过程,绘制在利普曼图上的实验数据表明,固溶体(PbxCa1-x)5(PO4)3(OH)在溶解初期按化学计量溶解,然后逐渐向上移动至Pb5(PO4)3OH的利普曼溶解曲线和饱和曲线,随后数据点沿利普曼溶解曲线从右向左移动。富含铅的(PbxCa1-x)5(PO4)3(OH)与富含钙的水溶液处于平衡状态。图形摘要25℃、初始pH为2.00时羟基氯磷灰石-羟基磷灰石固溶体[(PbxCa1-x)5(PO4)3OH]溶解的利普曼图。