Introduction

In recent years, the application of low-temperature catalytic oxidation of CO has become very important environmentally and industrially [13]. Au nanocatalysts, first reported by Haruta et al. [4], represent one of the most exciting research topics, providing great developments in the field of heterogeneous catalysis. It is therefore of great importance and also challenge to study the fundamentals of such complicated heterogeneous catalytic reactions [510]. Studies of surface science have become a successful strategy to define model catalysts effectively [1113]. Reports on reactions catalyzed by supported Au nanoparticles have shown that they are structurally sensitivity, and that different sizes of supported Au nanoparticles exhibit different catalytic performance. Briñas et al. [14] produced size-controllable Au colloids capped with glutathione by varying the pH before reduction. They suggested the use of a polymeric nanoparticle precursor. The density and size of such Au(I) glutathione polymers are dependent on pH: the higher the pH, the more thorough the hydrolysis of [AuCl4], strongly affecting the loading of Au in the Au/Al2O3 catalyst, as reported by Grisel et al. [15]. To study the deposition–precipitation process for Au/Al2O3 catalysts from aqueous HAuCl4, extended X-ray absorption fine structure (EXAFS) analysis was employed by Yang et al. [16], who observed that Au–Cl bonds with Au3+ ion were replaced by Au–OH on increasing the pH value of aqueous HAuCl4. In previous study [17], we observed that such pH-dependent speciation of aqueous HAuCl4 would influence the nucleation and growth of Au colloids. Although it is known that the pH value of aqueous HAuCl4 is a very important factor influencing the structure and properties of Au/SiO2 catalysts, the research into other influential factors is still lacking, particularly interelement effects.

In this work, we employed HAuCl4 with different reagents to adjust the pH to similar values to prepare Au colloids and Au/SiO2 catalysts, and compared the differences between these colloids and catalysts, which have different coexisting elements. Comparing Au/SiO2 catalysts produced with different pH values, we found great similarity when using the same coexisting elements.

Experimental Section

The concentration of HAuCl4 aqueous solution at pH 2.89, made from HAuCl4·4H2O (Au content, 47.8%), was measured to be 8.998 × 10−4 mol L−1 by inductively coupled plasma atomic emission spectrometry (ICP-AES). Four solutions with low pH values of 2.92 and 2.87 achieved by addition of NaCl (1.396 × 10−3 mol L−1, 10 mL) or chlorine aqueous solution (Cl concentration of 1.279 × 10−3 mol L−1, 10 mL) and with high pH values of 9.50 and 9.57 achieved by addition of NaOH aqueous solution (7.115 × 10−5 mol L−1, 8 mL) or ammonia solution (1.0 × 10−2 mol L−1, 9 mL) into 10 mL HAuCl4 aqueous solution were stirred and stabilized for 4–8 days, where the pH values varied within ±0.01. A series of NaCl aqueous solutions with different concentrations (as measured by ICP-AES) were prepared and used to plot a working curve for ion chromatography of Cl. These four HAuCl4 aqueous solutions are denoted as NaCl–HAuCl4, Cl2–HAuCl4, NaOH–HAuCl4, and NH3–HAuCl4, respectively.

Au colloids were produced by reducing these four aqueous HAuCl4 solutions by addition of ascorbic acid (VC) after addition of sodium benzenesulfonate (SDBS) [17], denoted as NaCl–Au colloid, Cl2–Au colloid, NaOH–Au colloid, and NH3–Au colloid, respectively.

Au/SiO2 catalysts were obtained in three steps. In the first step, the incipient wetness impregnation method was employed. The above four solutions with calculated amount of SiO2 (40–120 mesh, specific surface area 390 m2 g−1; Qingdao Haiyang Chemicals Company) were stirred and stabilized to obtain gold precursors. In the second step, dehydration of the four precursors at temperature of 80 °C for 12 h resulted in different solids, which were calcinated at 400 °C in air for 2 h in the third step. These catalysts are denoted as NaCl–Au/SiO2, Cl2–Au/SiO2, NaOH–Au/SiO2, and NH3–Au/SiO2, respectively.

A DELTA-320 pH-meter was used to measure the pH of aqueous solutions. The concentration of both HAuCl4 and NaCl was measured by inductively coupled plasma atomic emission spectrometry. A UV-2450 UV–Vis spectrophotometer was employed to obtain the UV–Vis absorption spectra of various solutions. Ion chromatography was carried out on a DX-120 using an AS14 column with mobile phase of Na2CO3 (3.5 × 10−3 mol/L) and NaHCO3 (1.0 × 10−3 mol/L) solution at flow rate of 1.2 mL min−1; the data were analyzed using XPS-PEAK41 software. Aqueous solution of HAuCl4 was filtered using a 0.45-µm micropore membrane before ion chromatography. A Dynapro-MS800 laser dynamic light scattering photometer was used to conduct dynamic light scattering (DLS) experiments. XRD spectra were acquired using a Philips X’PertPRO SUPER X-ray diffractometer with a Ni-filtered Cu Kα X-ray source operating at 40 kV and 50 mA. XPS measurements were performed using an ESCALAB 250 electron spectrometer with a monochromatized Al Kα excitation source ( = 1486.6 eV).

A fixed-bed flow reactor was employed to evaluate the catalytic activity of Au/SiO2. Au/SiO2 (100 mg) was fed into the reaction pipe through which gas consisting of 1% CO and 99% dry air went at 20 mL/min. We calculated a space velocity of \(12,000\,{\text{mL}}\,{\text{g}}^{ - 1}_{\text{cat}} {\text{h}}^{ - 1}\). The steady-state composition of the effluent gas was analyzed using an online GC-14C gas chromatograph (T = 80 °C, H2 carrier gas at 30 mL/min) equipped with a TDX-01 column during 30 min at desired reaction temperature. The conversion of CO was evaluated according to the integrated peak areas for CO and CO2, as follows:

$${\text{Activity}} = \frac{{A_{{{\text{CO}}_{2} }} }}{{A_{{{\text{CO}}_{2} }} + A_{\text{CO}} }} \times 100\,\%,$$

where \({A}_{{\rm CO}_{2}}\) and A CO are the peak area of CO and CO2 as monitored by the GC-14C gas chromatograph.

Results and discussion

Figure 1 shows the UV–Vis absorption spectra of NaCl–HAuCl4 (pH 2.92), Cl2–HAuCl4 (pH 2.87), NaOH–HAuCl4(pH 9.50), and NH3–HAuCl4 (pH 9.57). The maximum absorption peak of NaCl–HAuCl4 and Cl2–HAuCl4 was observed at 306 nm, which can be attributed to the two unresolved ligand (π)-to-metal (σ*) charge transfer (LMCT) transitions in [AuCl4] [14], whereas no obvious absorption was observed for NaOH–HAuCl4 or NH3–HAuCl4. The UV–Vis absorption spectra indicates that the speciation of aqueous HAuCl4 changed with pH [14].

Fig. 1
figure 1

UV–Vis absorption spectra of NaCl–HAuCl4, Cl2–HAuCl4, NaOH–HAuCl4, and NH3–HAuCl4

Ion chromatography was employed to quantitatively determine the speciation of NaCl–HAuCl4, Cl2–HAuCl4, NaOH–HAuCl4, and NH3–HAuCl4. Figure 2 shows ion chromatograms of aqueous NaCl with various Cl concentrations. The retention time of Cl was 3.8 min. A minus water peak always appears at ca. 1.88 min in the ion chromatograms. The Cl peak area (A) varied linearly with the Cl concentration ([Cl]) (Fig. 2, inset) as follows: A = 6.279 (±0.04) × [Cl] − 0.505 (±0.06). We employed XPS PEAK41 software to fit the ion chromatogram data [17].

Fig. 2
figure 2

Ion chromatograms with various Cl concentrations. Inset shows the linear dependence of the Cl peak area on the Cl concentration

Figure 3 shows the ion chromatograms of NaCl–HAuCl4, Cl2–HAuCl4, NaOH–HAuCl4, and NH3–HAuCl4. Detailed simulation results for the ion chromatograms of NaCl–HAuCl4 (A), Cl2–HAuCl4 (B), NaOH–HAuCl4 (C), and NH3–HAuCl4 (D) are summarized in Table 1. Table 2 summarizes the speciation of NaCl–HAuCl4 (A), Cl2–HAuCl4 (B), NaOH–HAuCl4 (C), and NH3–HAuCl4 (D) and the corresponding average formula [AuCl x (OH)4−x ] (x = 0 to 4). These ion chromatogram results are consistent with previous reports [17], confirming the speciation of these aqueous HAuCl4 solutions.

Fig. 3
figure 3

Ion chromatograms of NaCl–HAuCl4, Cl2–HAuCl4, NaOH–HAuCl4, and NH3–HAuCl4

Table 1 Detailed simulation results of ion chromatograms of NaCl–HAuCl4 (A), Cl2–HAuCl4 (B), NaOH–HAuCl4 (C), and NH3–HAuCl4 (D)
Table 2 Speciation of NaCl–HAuCl4 (A), Cl2–HAuCl4 (B), NaOH–HAuCl4 (C), and NH3–HAuCl4 (D)

These results clearly show that the Au species in aqueous HAuCl4 depend mostly on the pH value but are independent of the specific reagent used to adjust the solution pH. We studied the reduction of these four HAuCl4 solutions to synthesize Au colloids. Table 3 summarizes the DLS results for the Au colloid solutions synthesized from NaCl–HAuCl4, Cl2–HAuCl4, NaOH–HAuCl4, and NH3–HAuCl4. These results demonstrate that the average size and homogeneity of the obtained Au colloids also depended mostly on the pH value of the aqueous HAuCl4 but were independent of the specific reagent used to adjust the pH value.

Table 3 DLS results of Au colloid solutions synthesized from NaCl–HAuCl4, Cl2–HAuCl4, NaOH–HAuCl4, and NH3–HAuCl4

The ICP-AES analysis results showed that the Au loading in the Au/SiO2 catalysts prepared with any of the four HAuCl4 solutions was the same (1.9% weight ratio). Figure 4 shows the catalytic performance of the NaCl–Au/SiO2, Cl2–Au/SiO2, NaOH–Au/SiO2, and NH3–Au/SiO2 in CO oxidation from the room temperature to 180 °C. As the reaction temperature increased, the catalytic activity of the four catalysts first rose and then decreased. Such dependence of the catalytic activity on the reaction temperature was first found on Au/ZnO/SiO2 and Au/CeO2/SiO2 catalysts [18, 19]. We considered that the conversion of CO by catalytic oxidation was co-determined by two factors: weak chemical adsorption–desorption equilibrium on the catalyst surface, and the chemical reaction on the catalyst surface, which are strongly temperature dependent. At low temperature level, increasing the temperature has little influence on the weak chemical adsorption–desorption equilibrium on the catalyst surface, while the speed of the surface chemical reaction increases dramatically. Therefore, the CO catalytic oxidation conversion rate increased as the temperature increased from low to higher values; when the temperature reached a given level, the influence of further increase on the weak chemical adsorption–desorption equilibrium can no longer be neglected, as upon reaching this level, desorption of weakly chemisorbed species occurs and eventually becomes overwhelming, so the CO catalytic oxidation conversion rate declines with further temperature increase. The CO conversion rate for NaCl–Au/SiO2 reached 75 and 100% at room temperature (RT) and 85 °C, respectively, indicating better catalytic performance than that for Cl2–Au/SiO2. Although the catalytic performance of NaOH–Au/SiO2 was generally poorer than that of Cl2–Au/SiO2, they were similar at 85 °C. The conversion rate for NH3–Au/SiO2 was obviously poorer than for the other three catalysts. These results demonstrate that the catalytic performance of the Au/SiO2 catalysts not only depends on the pH value of the aqueous HAuCl4 but also has a close relationship with the specific reagent used to adjust the pH value.

Fig. 4
figure 4

Catalytic performance in CO oxidation of NaCl–Au/SiO2, Cl2–Au/SiO2, NaOH–Au/SiO2, and NH3–Au/SiO2

Figure 5 displays the stability of NaCl–Au/SiO2, Cl2–Au/SiO2, NaOH–Au/SiO2, and NH3–Au/SiO2 in CO oxidation at 85 °C. Under the tested conditions, the CO conversion of NaCl–Au/SiO2 and NaOH–Au/SiO2 remained stable, whereas that of Cl2–Au/SiO2 and NH3–Au/SiO2 decreased obviously. Although the size of NaCl–Au/SiO2 and Cl2–Au/SiO2 was similar, their stability differed. These results demonstrate that the stability of the Au/SiO2 catalysts depends mostly on the coexisting elements.

Fig. 5
figure 5

Stability of NaCl–Au/SiO2, Cl2–Au/SiO2, NaOH–Au/SiO2, and NH3–Au/SiO2 at 85 °C

Figure 6 displays the XRD patterns of NaCl–Au/SiO2 (A), Cl2–Au/SiO2 (B), NaOH–Au/SiO2 (C), and NH3–Au/SiO2 (D). The XRD patterns of the four catalysts all clearly show Au(111), Au(200), and Au(311) diffraction peaks. Using the Scherrer equation, the average crystalline size of Au in NaCl–Au/SiO2 (A), Cl2–Au/SiO2 (B), NaOH–Au/SiO2 (C), and NH3–Au/SiO2 (D) was estimated 15, 15, 20, and 22 nm, respectively. The catalytic activity and stability differed greatly between NaCl–Au/SiO2 (A) and Cl2–Au/SiO2 (B) and between NaOH–Au/SiO2 (C) and NH3–Au/SiO2 (D). However, the average crystalline size of the Au nanoparticles was similar, suggesting that the size of the Au nanoparticles is not the dominant factor affecting the catalytic activity and stability of these Au/SiO2 catalysts in CO oxidation, while the effect of the coexisting elements cannot be neglected.

Fig. 6
figure 6

XRD patterns of NaCl–Au/SiO2 (A), Cl2–Au/SiO2 (B), NaOH–Au/SiO2 (C), and NH3–Au/SiO2 (D)

Figure 7 displays the Au 4f XPS spectra of NaCl–Au/SiO2 (A), Cl2–Au/SiO2 (B), NaOH–Au/SiO2 (C), and NH3–Au/SiO2 (D), while Table 4 summarizes the peak-fitting results. The Au 4f XPS spectrum of NaOH–Au/SiO2 (C) could be well fit using one component centered at 84.0 eV, while the Au 4f XPS spectra of NaCl–Au/SiO2 (A), Cl2–Au/SiO2 (B), and NH3–Au/SiO2 (D) consisted of two components centered at 84.0 and 84.3 eV. We attribute this upward shift of the Au 4f binding energy to the lower size of the Au nanoparticles. The Au nanoparticles have controllable size because we used different reagents to adjust the pH value in the previous stage.

Fig. 7
figure 7

XPS patterns of NaCl–Au/SiO2 (A), Cl2–Au/SiO2 (B), NaOH–Au/SiO2 (C), and NH3–Au/SiO2 (D). Scattered circles and solid lines indicate experimental data and fit spectra, respectively

Table 4 Peak-fitting results of Au XPS spectra of NaCl–Au/SiO2 (A), Cl2–Au/SiO2 (B), NaOH–Au/SiO2 (C), and NH3–Au/SiO2 (D)

Conclusions

We successfully elucidated the speciation of aqueous HAuCl4 with different reagents used to adjust the pH value and researched its influence on the synthesis of Au colloids and Au/SiO2 catalysts. The Au species in aqueous HAuCl4 mostly depend on the pH value and are independent of the specific reagent used to adjust the pH value. The experimental results could be grouped into two sets: A (NaCl–HAuCl4), B (Cl2–HAuCl4) and C (NaOH–HAuCl4), D (NH3–HAuCl4). The average formula of aqueous HAuCl4 is [AuCl x (OH)4−x ], where x varies depending on the pH value (x = 0–4). At low pH (~2.9), x is high (x ≈ 3), whereas for high pH (~9.5), x is low (x ≈ 0.1). We employed aqueous HAuCl4 solutions with different reagents to adjust the pH value to synthesize Au colloids and Au/SiO2 catalysts through reduction and incipient wetness impregnation methods, respectively. The average size of the obtained Au colloids was positively correlated with the pH value of the aqueous HAuCl4 and was independent of the specific reagent used to adjust the pH value. The catalytic activity and stability of the Au/SiO2 catalysts not only depended on the pH value of the aqueous HAuCl4, but was also closely related to the specific reagent used to adjust the pH value initially. The lower the electronegativity, the better the catalytic activity and stability of the Au/SiO2 catalyst; the higher the electronegativity, the worse the catalytic activity and stability of the Au/SiO2 catalyst. The coexisting elements should be considered in future research, as they greatly affect the catalytic activity and stability of the catalysts.