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Synthesis and solubility of hopeite Zn3(PO4)2·4H2O


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Introduction

There are many known technologies for the remediation of sites contaminated by heavy metals. However, many of them are very expensive (e.g., removal of contaminated material), or these methods do not provide permanent solutions (e.g., encapsulation, vitrification). An alternative approach is to precipitate difficult-to-solubilize heavy metal phosphates by adding phosphorus compounds to contaminated soil to immobilize the metals and reduce their ecological bioavailability (Cotter-Howells 1996; Basta, McGowen 2004; Matusik et al. 2008; Zeng et al. 2020). The bioavailability of heavy metal ions such as Zn and Pb can be reduced by forming complexes of these metals with phosphorus compounds, thereby reducing their toxicity. The use of phosphorus compounds (apatite, among others) causes the transition of heavy metal ions from readily available forms to permanently bound forms of these metals (Manecki et al. 2006). Several minerals with varying degrees of solubility and, thus, stability are then formed. These include pyromorphite, hydroxypyromorphite and hopeite. To predict the mobility of heavy metal compounds bound in the form of phosphates, a solubility test is performed on the mineral to determine its solubility product Ksp. The smaller the value of Ksp, the greater the stability of a mineral.

The mobility of Zn compounds can be controlled by the solubility of hydrated zinc phosphate, hopeite Zn3(PO4)2·4H2O. The formation of Zn phosphates in contaminated soils would help immobilize this metal in the soil. To predict the mobility of Zn compounds bound as phosphates, the solubility of hopeite, the most common reaction product of Zn and PO43–, was measured for the first time by Nriagu (1973). He performed an experiment to dissolve hopeite in dilute solutions of phosphoric acid at 25°C. Analysis of the data in terms of a model that assumed the formation of an ionic pair of ZnHPO40 and ZnH2PO4+ allowed the determination of the solubility product Ksp for α-hopeite, which was log Ksp = −35.3 ± 0.1 (Nriagu 1973). In our proposed study, Ksp was determined in an aqueous solution at pH 2.0 obtained by using dilute nitric acid. Based on the determined Ksp value, we calculated the free energy of formation ΔG°f,298, a parameter that has not been determined before. The results will allow us to assess the stability of hopeite, which can be formed by the reaction of phosphorus compounds added to wastewater and soils contaminated with zinc compounds.

Material and Methods
Synthesis of hopeite Zn3(PO4)2·4H2O

To synthesize 10 g of hopeite, 14.4 g of Zn(CH3COO)2·2H2O and 5.9 g of K2HPO4 were individually dissolved in 500 mL of redistilled water at 25°C. Using a peristaltic pump, these solutions were gradually and simultaneously mixed into a 3 L beaker filled with 1.5 L of continuously stirred redistilled water. The hopeite synthesis reaction proceeded according to the reaction: 3(Zn(CH3COO)2)2H2O+2KH2PO4=Zn3(PO4)24H2O+2CH3COOK+6H2O $$\matrix{ {3\left( {{\rm{Zn}}{{\left( {{\rm{C}}{{\rm{H}}_3}{\rm{COO}}} \right)}_2}} \right) \cdot 2{{\rm{H}}_2}{\rm{O}} + 2{\rm{K}}{{\rm{H}}_2}{\rm{P}}{{\rm{O}}_4} = {\rm{Z}}{{\rm{n}}_3}{{\left( {{\rm{P}}{{\rm{O}}_4}} \right)}_2} \cdot 4{{\rm{H}}_2}{\rm{O}}} \hfill \cr {\quad + 2{\rm{C}}{{\rm{H}}_3}{\rm{COOK}} + 6{{\rm{H}}_2}{\rm{O}}} \hfill \cr } $$

A white precipitate appeared immediately upon mixing. The suspension lasted four days after the Zn and PO4 solutions were exhausted. It was then decanted, filtered, and washed with redistilled water and acetone. The residue was dried at 110°C for 12 h.

Precipitate and solution characterization

X-ray diffraction (XRD) analysis was performed on a SmartLab RIGAKU diffractometer using a copper X-ray tube in the angular range of 5–70°2θ with a 0.05°2θ measuring step. The PCPDFWIN version 1.30, formalized by JCPDSICDD, was used to identify mineral phases. Scanning electron microscopy (SEM) was performed using an FEI QUANTA 200 FEG microscope with an Energy Dispersive Spectrometer (EDS) on uncoated samples. Zn concentrations were measured by atomic absorption spectroscopy (AAS) method using a SavantAA GBC spectrometer. PO4 concentrations were determined colorimetrically by the molybdenum blue method (Lenoble et al. 2003) using a Hitachi 1600 spectrophotometer at 870 nm wavelength.

Dissolution experiments

Dissolution experiments were conducted at 25°C with initial pH values of 2.0. 200 mg aliquot of synthetic Zn3(PO4)2·4H2O was added to 250 mL of 0.05 M KNO3, and the pH was adjusted to the desired value using 0.1 M HNO3. The experiment was conducted in triplicate in unbuffered suspensions. In each case, the pH drifted freely after setting the initial value. To determine that equilibration had been reached, samples of the reaction solutions were taken after 1, 2, 4, and 8 hours and after 1, 2, 4, 7, 14, and 30 days. The suspension bottles were shaken twice a week and always after sampling. For each sample, the solids were allowed to settle before 7 mL of the supernatant was withdrawn, without refilling with the solution afterward. The samples were analyzed for pH (combined glass electrode), Zntot (AAS) and P(V)tot (UV-Vis). Solubility product calculations were performed using the computer program PHREEQC with a modified MINTEQ. v4 thermodynamic database (Allison et al. 1991). The activities of ionic species were calculated from measured concentrations of elements by applying the Davies equation or the extended Debye-Huckel equation.

Results and Discussion
Solid characterization

The white precipitate produced in the synthesis is identified as the hopeite Zn3(PO4)2·4H2O by comparing peak positions with those of hopeite reported in Joint Committee on Powder Diffraction Standards (JCPDS) cards 33-1474. All peaks produced by the precipitate are identified as hopeite peaks (Fig. 1).

Figure 1.

XRD pattern of synthetic hopeite.

The SEM observations indicate that the precipitate is composed mainly of 10–100 μm grains. Among these grains, idiomorphic crystals in the form of a rectangular shape reach lengths up to 200 μm (Fig. 2). The surface of the grains is smooth. The crystals are composed of Zn, P, O as determined by EDS.

Figure 2.

Scanning electron microscope (SEM) image of synthetic hopeite.

Dissolution experiments

In the dissolution experiments, most of the reaction occurred within two days with dissolution rates, as indicated by the increase in zinc and phosphate concentrations, declining with time. The evolution of the solution composition over time is shown in Figure 3. The hopeite dissolved stoichiometrically. Hopeite was assumed to be in equilibrium with the solution when the concentrations of Zn and PO4 in three consecutive samples of the test solution were equal within an error measured by twice the standard deviation. To determine the congruence of the dissolution of hopeite, as a prerequisite for determining the solubility coefficient, it was necessary to determine the equilibrium state for Zn2+ and PO43- concentrations. For this purpose, the last five concentration values for both ions within the error limit were considered. The equilibrium concentration for Zn2+ was 2.117 ± 0.04, and for PO43- was 1.432 ± 0.012, i.e. the molar ratio of the two Zn : PO4 ions is 1.48 ± 0.03. The calculated molar ratio of the ions in the aqueous solution studied was 3:2 and is consistent with the chemical formula of hopeite Zn3(PO4)2·4H2O. The dissolution of hopeite was congruent, meaning that the mineral dissolved without forming solid secondary phases.

Figure 3.

Concentrations of Zn and PO4 in the dissolution experiment with an initial pH of 2.0 (equilibrium pH 4.8) and temperature of 25°C.

The ion activity product (IAP) for the dissolution reaction of hopeite Zn3(PO4)24H2O3Zn2++2PO43+4H2O $${\rm{Z}}{{\rm{n}}_3}{\left( {{\rm{P}}{{\rm{O}}_4}} \right)_2} \cdot 4{{\rm{H}}_2}{\rm{O}} \Leftrightarrow 3{\rm{Z}}{{\rm{n}}^{2 + }} + 2{\rm{P}}{{\rm{O}}_4}^{3 - } + 4{{\rm{H}}_2}{{\rm{O}}^ * }$$ * activity for H2O is 0, so it is not taken into account in further calculations can be written as logIAP=3log{ Zn2+ }+2log{ PO43 } $$\log {\rm{IAP}} = 3\log \left\{ {{\rm{Z}}{{\rm{n}}^{2 + }}} \right\} + 2\log \left\{ {{\rm{P}}{{\rm{O}}_4}^{3 - }} \right\}$$ where brackets denote activities. At equilibrium, the IAP is equal to the solubility product, Ksp. Based on measured concentrations and pH at equilibrium, Zn2+ and PO43- activities were calculated using the computer program PHREEQC. Based on the calculated activities, the log IAP was calculated using Eq. (3). The equilibrium log IAP from the experiments, represents the log Ksp at 25°C and equals –35.72 ± 0.03. This value agrees well with the log Ksp = –35.29 ± 0.1 Nriagu (1973) reported.

Based on the solubility product determined for hopeite in the experiments, the Gibbs free energy of formation ΔG°f(hopeite) is calculated. The Gibbs free energy ΔG°r of dissolution reaction (2) is expressed by the equation ΔGr=3ΔGf(Zn2+)+2ΔGf(PO43)+4ΔGf(H2O)ΔGf (hopeite)  $$\matrix{ {{\rm{\Delta G}}_{\rm{r}}^ \circ } \hfill & { = 3{\rm{\Delta G}}_{\rm{f}}^ \circ \left( {{\rm{Z}}{{\rm{n}}^{2 + }}} \right) + 2{\rm{\Delta G}}_{\rm{f}}^ \circ \left( {{\rm{PO}}_4^{3 - }} \right) + 4{\rm{\Delta G}}_{\rm{f}}^ \circ \left( {{{\rm{H}}_2}{\rm{O}}} \right)} \hfill \cr {} \hfill & { - {\rm{\Delta }}G_f^ \circ {\rm{\;(hopeite)\;}}} \hfill \cr } $$ is, at equilibrium, related to the solubility product Ksp as follows: ΔGr=RTlnKsp $${\rm{\Delta G}}_{\rm{r}}^ \circ = - {\rm{RTln}}{{\rm{K}}_{{\rm{sp}}}}$$ where R is the gas constant (8.314472 J mol−1 K−1), and T is the temperature (298.15 K). This gives a value for ΔG°r of 203.9 ± 0.1 kJ mol−1. Calculation of the Gibbs free energy of the formation of hopeite is enabled by equation 3 as follows: ΔGf (hopeite) =3ΔGf(Zn2+)+2ΔGf(PO43)+4ΔGf(H2O)+RTInKsp $$\matrix{ {{\rm{\Delta G}}_{\rm{f}}^ \circ {\rm{\;(hopeite)\;}} = 3{\rm{\Delta G}}_{\rm{f}}^ \circ \left( {{\rm{Z}}{{\rm{n}}^{2 + }}} \right) + 2{\rm{\Delta G}}_{\rm{f}}^ \circ \left( {{\rm{P}}{{\rm{O}}_4}^{3 - }} \right)} \hfill \cr {\quad + 4{\rm{\Delta G}}_{\rm{f}}^ \circ \left( {{{\rm{H}}_2}{\rm{O}}} \right) + {\rm{RTIn}}{{\rm{K}}_{{\rm{sp}}}}} \hfill \cr } $$

Based on available values of ΔG°f(Zn2+) = −147.30 ± 0.2, ΔG°f(PO43−) = −1001.60 ± 0.9, and ΔG°f(H2O) = −237.1 ± 0.1 kJ mol−1 from Robie et al. (1978) and the value of Ksp = −35.72 ± 0.03 experimentally determined above, the Gibbs free energy of formation of hopeite may be calculated as ΔG°f(hopeite) = −3597.4 ± 1.0 kJ mol−1.

Conclusions

Experiments conducted by Nriagu (1973) indicated that Zn ions are rapidly converted to hopeite in dilute phosphate solutions. Therefore, hopeite is believed to be the possible end product of Zn released to the environment. Hopeite is the most stable zinc phosphate that could be crystallized from the system. It is a thermodynamically stable mineral, thus controlling the mobility of zinc in contaminated soils remediated with phosphate compounds and fertilizers.

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