Effects of Surfactants on High Regularity of 3D Porous Nickel for Zn<sup>2+</sup> Adsorption Application

Guo, Xiaogang; Li, Xueming; Zheng, Yonghong; Lai, Chuan; Li, Wulin; Luo, Binbin; Zhang, Daixiong

doi:https://doi.org/10.1155/2014/358312

Journal of Nanomaterials

On this page

Abstract Introduction Materials and Methods Results and Discussion Conclusions Acknowledgments References Copyright Related Articles

Special Issue

Nanomaterials for Environmental Applications

View this Special Issue

Research Article | Open Access

Volume 2014 | Article ID 358312 | https://doi.org/10.1155/2014/358312

Effects of Surfactants on High Regularity of 3D Porous Nickel for Zn²⁺ Adsorption Application

Xiaogang Guo,¹Xueming Li,¹Yonghong Zheng,²Chuan Lai,¹Wulin Li,¹Binbin Luo,¹and Daixiong Zhang¹

Academic Editor: Fan Dong

Received23 Nov 2013

Revised13 Jan 2014

Accepted15 Jan 2014

Published18 Mar 2014

Abstract

Three-dimensional porous nickel (3D-PN) film with large specific surface area () and high porosity has been successfully prepared by hydrogen bubble dynamic template (HBDT) method. This work presents the effects of PEG 10000 and 1,4-butynediol as new additive combination on surface morphology of the PN film. Meanwhile, the application of 3D-PN in Zn²⁺ adsorption was preliminarily investigated in the paper. The surface area is determined as large as 166.7 cm²/mg and the porosity is 0.762 when the concentration of PEG 10000 and 1,4-butynediol was 0.3 g/100 mL and 0.1 g/100 mL, respectively. The adsorption capacity ( and (%)) of PN for Zn²⁺ is observed to be 9.145 mg/g and 0.691 for Zn(NO₃)₂·6H₂O. The morphology and the microstructure, the product formation, the the concentration of the metal ions were characterized by scanning electron microscopy (SEM), X-ray powder diffraction (XRD), electrochemical impedance spectroscopy (EIS), and atomic absorption spectrometry (AAS), respectively.

1. Introduction

Three-dimensional (3D) porous metals (Ni, Cu, Sn, etc.) [1–4], with highly porous dendritic walls and numerous nanoparticles, are considered as promising nanomaterials due to their importance to both academic study and technological applications in separation systems [5], sensors [6, 7], fuel batteries [8, 9], electrochemistry [10, 11], electronic materials [12], and high performance supercapacitors [13]. Many researchers have successfully developed the 3D porous metal films electrode materials by template-directed synthesis method. And commonly used templates are considered such as liquid crystal, high internal phase emulsion (HIPE), photonic crystals, porous polycarbonate membranes [14, 15], anodic alumina membranes [16], colloidal crystals [17], and echinoid skeletal structures [18]. Compared with other approaches, hydrogen bubble dynamic template (HBDT) with hydrogen bubbles as the template on the cathode at high current densities is the green and promising one with lots of advantages: low-cost equipment, controllable structure, facile one-step synthesis process, and easy elimination of the template [11, 19].

Recently, many efforts have been devoted to improving the morphology and developing performance of porous metal films, especially preparation of high surface area of three-dimensional porous nickel (3D-PN) films and application of their alloys in catalysis aspect and electrochemical pseudocapacitors. For example, Šimpraga et al. obtained a very high roughness factor value of the order of 2800 for Ni-Fe composite electrode prepared by simple electrochemical co-deposition process [20]. Rausch and Wendt described the high surface area sintered Ni and Raney Ni for their electrocatalytic properties [1, 21]. This mesoporous material was used as a positive electrode in hybrid supercapacitors/battery systems. Recently, the preparation of a highly porous large surface area nickel has been reported by Brown and Sotiropoulos [22]. Moreover, the nickel foam-supported porous Ni(OH)₂/NiOOH composite film application for advanced pseudocapacitor material was studied by Yuan et al. [23]. However, how to control the bubble size to easily obtain attractive structure is still a great challenge.

The treatment of metal-contaminated wastewater has always been a serious issue in mining, electroplating, and the chemical and electronic industries. The impact of toxic heavy metal ions on health and on the environment has been widely reported. Metal ion treatment by adsorption into porous materials has attracted considerable attention due to their high efficiencies and economic feasibility [24, 25]. For instance, active carbon is often used to adsorb heavy metal ions and other toxic chemicals [25, 26]. Since the adsorption ability of porous materials can to a large extent be attributed to their high porosity, the adsorption ability of PN should be improved if there are suitable additives or additive combination. However, there are few studies on depollution of environment by the 3D-PN.

In electroplate industry, surfactants have been widely used as stabilizers in aqueous media to alter the surface tension of the sol/gas and protect the bubbles from coalescence. Therefore, a highly stable, well-dispersed bubble template can be obtained [27, 28]. However, there has been very little research on the effects of additive on the surface of PN film. Meanwhile, the mechanism of additive is not yet fully understood.

The research objectives of this study include first, fabricating 3D-PN film by HBDT method; second, developing 3D-network structure of PN film with the novel additive combination (PEG 10000 and 1,4-butynediol) and undertaking preliminary exploration of the impacting mechanism of additives on the morphology of PN films. In addition, the application of 3D-PN film for Zn²⁺ adsorption has been investigated in this paper, which is built upon previous respectable attempts.

2. Materials and Methods

2.1. Materials and Reagents

The electrolyte consisted of nickel sulfate, ammonium chloride, concentrated sulfuric acid, and boric acid, with the new additive combination of PEG 10000 and 1,4-butynediol. Zinc nitrate hexahydrate (Zn(NO₃)₂·6H₂O) was prepared for Zn²⁺ adsorption. All the regents mentioned were of analytical grade. Cooper plate and nickel plate were purchased from Shanghai Jinan Metal Product Co., Ltd. (Shanghai, China), respectively. In the process of deposition, the solution was kept stationary. Deionized water was used throughout the experiment.

2.2. Electrode Preparation

In the study, a thin sheet of copper (99.99%) was selected for the cathode substrate material, which was repeatedly polished to highlight by numbers 400, 600, 800, and 1000 metallographic sandpaper in flowing water, cut into an area of 0.01 m × 0.05 m, and then sealed by insulating epoxy resin; only a 0.01 m × 0.01 m surface exposed to the electrolyte was kept, and a nickel plate (99.99%) with more than 0.03 m² acted as anode material. The distance between the two electrodes was 1 cm. Before electrodeposition, the copper substrate was dried in ovens at 150°C for 10 min, cooled to room temperature, and weighed; then the thickness of the area to be electroplated by micrometer screw was measured. And both cathode and anode were washed with deionized water in the CNC ultrasound and successively treated in the 45 g/L Na₂CO₃, 45 g/L NaOH, and 45 g/L Na₂SO₄ to remove oil; then they were immediately etched in hydrochloric acid for rough surface and then washed with deionized water. Deposition was performed in a stationary electrolyte solution (without stirring or N₂ bubbling). And it should be stressed that 3D-PN film was soaked in water for 2 min at 30°C after rinse for 1 min with deionized water. Then it was left to dry to remove residual impurities and water in constant temperature oven at 80°C for 90 min; the film was used for Zn²⁺ adsorption. All the experiments and measurements were carried out at room temperature (25 ± 1°C).

2.3. Electrolyte and Operating Conditions Preparation

In this paper, the optimal process conditions were determined by previous experience and orthogonal test with six factors of the concentration of nickel sulfate, ammonium chloride, sulfuric acid, boric acid, cathode current density, and deposition time. In order to express easily and intuitively, the six factors above were successively referred to as , , , , , and , which were generally considered to be the most important factors. Optimization of the suitable 3D-network structure can be carried out by a giant amount of research. And optimal compositions and operating conditions of the basic electrolyte were shown in Table 1. However, it was found that 3D structure of PN film was not obvious enough without additives. As shown in Table 2, different concentrations of additives (thePEG 10000 and 1,4-butynediol) were considered to be added to the electrolyte and this modificatory PN film was obtained with high specific surface area and porosity. Meanwhile, the schematic diagram of formation of PNF supported on Cu substrate was shown in Scheme 1.

2.4. Porosity and Surface Area Measurements

2.4.1. Porosity Measurements

The analytical balance was used to weigh the mass of copper substrate before deposition of the PN film and after electrodeposition process. The film was dried in oven and then reweighed. With micrometer screw, we can determine the thickness of PN film and analyze mass variation of electrodeposition process to calculate porosity of the sample preparation. The formula was where is the mass specimen weight (mg), is the density of nickel (g/cm³), is PN film thickness (cm), and is the contact area of the test piece and the bath (cm²).

2.4.2. Surface Area Measurements

In the study, the (specific surface area of the electrode) was performed by using electrochemical impedance spectrum (EIS) on CHI660B electrochemical workstation. Originally, the working electrode was held at −1.50 V (versus SCE) for 30 min in order to reduce the film on the electrode surface and a reproducible electrode surface could be obtained. A three-electrode test cell was used with the As-prepared PN film as working electrode, platinum foil as the counter, and a saturated calomel electrode (SCE) as the reference electrode. The sulfuric acid solution (0.5 mol/L) was used as the test solution. The EIS measurement was carried out in the frequency range from 100 kHz to 0.01 Hz under AC stimulus with 5 mV of amplitude and no applied voltage bias, which was performed on CHI660B electrochemical workstation. Subsequently, using Z-view software to fit initial EIS data, we can calculate the differential capacitance . Therefore, specific surface area of the electrode is [29]: where is the surface area of specimen and .

2.4.3. Environmental Applications of 3D-PN Film

Zinc nitrate solution (50 mg/L) was prepared to simulate the heavy metal ions (Zn²⁺) in sewage. As-prepared PN film fabricated under identical optimal conditions was added into 100 mL zinc nitrate solution stirred at 120 r/min by ITCES (intelligent temperature control electromagnetic stirrer) at 25 ± 1°C. After the adsorption process, the flame atomic absorption spectrometry was used to determine the concentration of the metal ions with a standard calibration curve [30]. The mass of adsorbent could be determined by weighing the mass of cathode substrate before and after electrodeposition, respectively. Significant factors of porous nickel on the sewage purification treatment were shown in Table 3. Purification effect can be calculated by the following formulas: where (mg/g), (mg/g), (mg/L), (mg/L), (mg/L), (g), (%), and (L) represent the adsorption capacity after a certain period of time, the equilibrium adsorption capacity, the initial concentration, adsorption equilibrium concentration of ions, concentration of ions after a certain period of time, the sorbent mass, purifying rate, and solution volume separately.

2.4.4. SEM, XRD, and AAS Measurements

The surface morphology of as-prepared electrodes was investigated by scanning electron microscopy (SEM) (TESCAN VEGA II LMU). Crystallographic structure was studied by X-ray diffraction (XRD) using an X-ray diffraction using an automatic XRD analyzer (XRD-6000 Lab X SHIMADZU) with monochromatic Cu radiation ( nm) from 10° to 80° at a speed of 4°/min. Additionally, the accelerating voltage and emission current of the XRD were, respectively, 40 kV and 30 mA. And the concentration of the zinc ion after the adsorption process was determined by atomic absorption spectrometry (AAS, 180-80 atomic absorption spectrophotometer, Hitachi, Japan) with detection wavelength of 214 nm and width of slit of 1.3 nm, respectively.

3. Results and Discussion

3.1. Effect of the PEG 10000

Figure 1 showed the surface morphology figures of PN film obtained in the electrode position of 25 s under different concentrations of PEG 10000 and fixed current density (4 A/cm²) at the room temperature (25 ± 1°C). Meanwhile, the constituents of the electrolyte were illustrated in Table 1. And Figure 1 showed the porous structure obviously formed on the surface of the as-prepared nickel film when the concentration of the additive PEG 10000 was 0.01 g/100 mL in the electrolyte. However, the structure of hole wall of the PN film significantly changed when the concentration of that increases gradually to 0.05 g/100 mL. The diameter of main holes increased to about 10 microns and hole wall thickness decreased. Meanwhile, the grains were refined, hole density increased gradually, and surface area calculated by formula (2) also increased according to Figure 2. It should be noted that membrane structure of the prepared PN was transformed into a 3D structure one. However, relatively more amount of additive to some extent gradually destroyed 3D structure while the concentration of PEG 10000 exceeded 0.07 g/100 mL; this could be the reason of a certain effect of nickel ions and hydrogen ions reduction reaction. And Figure 2 showed that porosity had a trend of decreasing sharply along with the increase of PEG 1000 concentration. When the amount of additive was 0.05 g/100 mL, PN film with the uniform distribution reached maximum specific surface area with relatively high porosity (Figures 1(b) and 1(e)). Therefore, the required optimization characteristics of PN film should be prepared by controlling the amount of additive PEG 10000.

(a)

(b)

(c)

(d)

(e)

(f)

3.2. Effect of the 1,4-Butynediol

Figure 3 presented the surface morphology outline of PN film in the base plating solution of 0.2 mol/L nickel sulfate, 1.2 mol/L boric acid, 0.9 mL/100 mL concentrated sulfuric acid, and 1.5 mol/L ammonium chloride with different concentrations (0.01~0.05 g/100 mL) of 1,4-butynediol. The temperature and current density were the same as above. When adding 0.01 g/100 mL of 1,4-butynediol into electrolyte, 3D porous structure was obviously seen in Figures 3(a) and 3(d). Figure 4 showed that the porosity decreased with the concentration of 1,4-butynediol increasing (from 0.01 g/100 mL to 0.05 g/100 mL). Meanwhile, the variation tendency of porosity in Figure 4 was similar to that affected by PEG 10000 as well. However, new complex structure similar to the leaves emerged on the PN film surface with increasing concentration. Meanwhile, hole wall became thicker and sedimentary layer of dendrite coarsened. The smaller aperture was associated with the fast release rate of hydrogen bubble, resulting in an acceleration of reduction of Ni²⁺ speed-up, which also explained why dendrite of the coating coarsened. However, network structure of 3D-PN film will disappear (Figures 3(c) and 3(f)) when the concentration of additive 1,4-butynediol increases to a certain extent. Therefore, 1,4-butynediol could be also the optional additive to obtain the 3D-PN film with high surface area and appropriate porosity.

(a)

(b)

(c)

(d)

(e)

(f)

(a)

(b)

(c)

(d)

(e)

(f)

3.3. Synergy Effect of PEG 10000 and 1,4-Butynediol

Top-view SEM images of the synergy effect of 1,4-butynediol and PEG 10000 on PN film were shown in Figure 5. The concentration of 1,4-butynediol was controlled at 0.01 g/100 mL. With the concentration of PEG 10000 continuing to increase (from 0.01 to 0.05 g/100 mL), the hole wall of as-prepared PN film became thicker anddendrites of deposits coarsened, which was similar to the complex structure of the leaves. If the concentration of PEG 10000 was larger than 0.05 g/100 mL, a mesh and irregular structure came into being in PN film, which was largely because of some inhibitory effect of PEG 10000 on reduction reaction of nickel ions and hydrogen ions. It can be obviously seen from Figures 5(b)–5(f) that the aperture can increase to 12 microns (then decrease) and relatively homogeneous distribution. On the other hand, at level 3 reached a maximum of 140.8 mg/cm² with sharp decline and 3D structure will be gone by continuously adding the 1,4-butynediol. The 3D-PN film with a maximum of (166.7 cm²/mg > 140.8 cm²/mg) and porosity (0.762) was obtained when the concentration of PEG 10000 and 1,4-butynediol was 0.03 g/100 mL and 0.01 g/100 mL (Figure 6). As mentioned, tracing changes of concentration of PEG 10000 or 1,4-butylglycol could adjust and control porous structure of nickel film. And similar study about 3D porous structure with the additive was reported by Huang et al. [31]. Moreover, the more ideal 3D-PN film was fabricated by HBDT with the additive combination of PEG 10000 and 1,4-butynediol added into electrolyte. In this paper, the additive PEG 10000 with certain adsorption of metal cations [32] and good hydrophilicity because of hydrogen bond can decrease interfacial tension between the hydrogen bubble and the cathode plate (Scheme 1) and directionally align in the form of meandering structure in the solution. And as a kind of gemini surfactant, the 1,4-butynediol with ideal solution interface adsorption capacity could depress rapid accumulation of hydrogen bubble (Scheme 1) and bubble size increase and largely promote the migration rate of the hydrogen bubble from cathode plate to the solution interface. Meanwhile, the additives PEG 10000 and 1,4-butynediol with a certain concentration ratio (PEG 10000: 1,4-butynediol = 3 : 1) appeared to have optimal activity to regulate the surface photography of 3D-PN film instead of mixing them together randomly. Bernardes et al. [33] observed that a cosurfactant such as decanol can induce a lamellar structure. Polymer surfactant could effectively block mutual adsorption among particles, mainly relying on the solvation layer of polymer. It was worth mentioning that there was no reaction between PEG 10000 and 1,4-butynediol. Meanwhile, when the additives (PEG 10000 and 1,4-butynediol) influenced the structure of PN film simultaneously, the final effect was better than the simple individual effect, which was the key reason why the 3D structure of PN film was optimized by changing their concentrations at different levels. Therefore, the reticular 3D structure of PN film was prepared by HBDT method by controlling the concentration of the novel additive combination (Table 2).

This result was further supported by XRD spectrum. As shown in Figure 7, all of the diffraction peaks were indexed at different temperatures. The characteristics of the face-centered cubic (fcc) nickel crystal structure was evident as indicated by the orientations along the Ni (111), Ni (200), and Ni (220) directions. It was obvious that the feature peak of the copper in the X-ray diffraction pattern was caused by the copper substrate, and both the crystalline and the intensity ratios of nickel can vary with temperature. These results indicated that dentritic nickel is abundant in facets. It has been known that more facets with a slower growth rate would be exposed on the crystal surface and consequently exhibit relatively stronger diffraction intensity in the corresponding XRD pattern [34]. The intensity ratio between the (111) and (200) diffraction peaks was higher than the ratio of other peaks, especially at 25°C. These strong and sharp peaks indicated that the obtained Ni crystals were highly crystalline. No detectable diffraction peaks of impurities such as copper oxide or nickel oxide signified the high purity and stability of the as-obtained products.

3.4. Adsorption Behavior of PN Film for Simulated Wastewater (Zn²⁺)

The PN film with high specific surface area prepared under optimal conditions exhibited certain advantages in sewage purification. Figure 8 showed surface morphology of before and after adsorption of heavy metal ions (Zn²⁺). Compared with Figure 8(b), rough and glistening areas in the direction of arrows in Figure 8(a) were confirmed as the adsorbed Zn²⁺. At the same time, the reliability of the zinc absorption was further demonstrated by AAS. Time-variation tendencies of and (%) of adsorption process of Zn²⁺ were clearly shown in Figures 9 and 10. Meanwhile, Figure 10 presented the concentration changes of Zn²⁺ during the adsorption process. The purification effect was continuously improved with the increase of time, especially in the first dozens of seconds. As time increased, the concentration of Zn²⁺ had reached equilibrium value. Meanwhile, gradually increased until maximum value () of 9.145 mg/g for Zn(NO₃)₂·6H₂O concentrations over 5 mg/L and (%) 0.691, concentration of the purified sewage basically to tend stable limited to surface effective adsorption sites when the adsorption time continued to increase. The adsorption rate of PN with large specific surface area and porous structure of overlapping layers was more rapid than that of granular porous adsorbent in adsorbing heave metal ions, contributing to reaching adsorption equilibrium within a short time. It is needed to be emphasized that the time elapsed for the Zn²⁺ adsorption to reach its maximum was about 10 min for the PN and there was no nickel ions in the zinc nitrate solution after adsorption equilibrium detected by AAS.

(a)

(b)

4. Conclusions

The PN film with reticular 3D network structure has been successfully fabricated by HBDT, adding novel additive combination (PEG 10000 and 1,4-butynediol) into the electrolyte. Meanwhile, the PN film with high specific surface area ( cm²/mg) and high porosity (0.762) had open interconnected macroporous walls. The experiment conditions were optimized such that the concentration of nickel sulfate, ammonium chloride, concentrated sulfuric acid and boric acid, PEG 10000, 1,4-butynediol, cathode current density, and deposition time were 0.2 mol/L, 1.5 mol/L, 0.9 mL/100 mL, 1.2 mol/L, 0.3 g/100 mL, 0.1 g/100 mL, 4.0 A/cm², and 25 s, respectively, which were determined by SEM microscopic image analysis and extensive explorations. Meanwhile, the sewage (Zn²⁺) purification of 3D-PN was investigated in this study. Adsorption capacity ( and (%)) of PN for Zn²⁺ can reach 9.145 mg/g and 0.691 for Zn(NO₃)₂·6H₂O concentrations over 5 mg/L, which provided the possibility of the novel application of 3D-PN or other porous metals.

Conflict of Interests

The authors declare that there is no conflict of interests regarding the publication of this paper.

Acknowledgments

This work was supported by the National Natural Science Foundation of China (no. 61271059), the Natural Science Foundation Project of Chongqing (no. 2010BB4246), and the Science and Technology Development Project of Chongqing (no. CSTC2012gg-yyjs90007).

References

P. A. Nelson and J. R. Owen, “A high-performance supercapacitor/battery hybrid incorporating templated mesoporous electrodes,” Journal of the Electrochemical Society, vol. 150, no. 10, pp. A1313–A1317, 2003.
View at: Publisher Site | Google Scholar
H.-C. Shin and M. Liu, “Copper foam structures with highly porous nanostructured walls,” Chemistry of Materials, vol. 16, no. 25, pp. 5460–5464, 2004.
View at: Publisher Site | Google Scholar
H.-C. Shin, J. Dong, and M. Liu, “Porous tin oxides prepared using an anodic oxidation process,” Advanced Materials, vol. 16, no. 3, pp. 237–240, 2004.
View at: Google Scholar
H.-C. Shin, J. Dong, and M. Liu, “Nanoporous structures prepared by an electrochemical deposition process,” Advanced Materials, vol. 15, no. 19, pp. 1610–1614, 2003.
View at: Publisher Site | Google Scholar
K. Kusakabe, T. Kuroda, A. Murata, and S. Morooka, “Formation of a Y-type zeolite membrane on a porous α-alumina tube for gas separation,” Industrial and Engineering Chemistry Research, vol. 36, no. 3, pp. 649–655, 1997.
View at: Google Scholar
A. Salehi and D. Jamshidi Kalantari, “Characteristics of highly sensitive Au/porous-GaAs Schottky junctions as selective CO and NO gas sensors,” Sensors and Actuators B: Chemical, vol. 122, no. 1, pp. 69–74, 2007.
View at: Publisher Site | Google Scholar
G. Zhang, C. Li, F. Cheng, and J. Chen, “ZnFe₂O₄ tubes: synthesis and application to gas sensors with high sensitivity and low-energy consumption,” Sensors and Actuators B: Chemical, vol. 120, no. 2, pp. 403–410, 2007.
View at: Publisher Site | Google Scholar
L. Wang, H. W. Xu, P. C. Chen, D. W. Zhang, C. X. Ding, and C. H. Chen, “Electrostatic spray deposition of porous Fe₂O₃ thin films as anode material with improved electrochemical performance for lithium-ion batteries,” Journal of Power Sources, vol. 193, no. 2, pp. 846–850, 2009.
View at: Publisher Site | Google Scholar
L. Yuan, Z. P. Guo, K. Konstantinov, H. K. Liu, and S. X. Dou, “Nano-structured spherical porous SnO₂ anodes for lithium-ion batteries,” Journal of Power Sources, vol. 159, no. 1, pp. 345–348, 2006.
View at: Publisher Site | Google Scholar
J.-Y. Li, S. Xiong, J. Pan, and Y. Qian, “Hydrothermal synthesis and electrochemical properties of urchin-like core-shell copper oxide nanostructures,” Journal of Physical Chemistry C, vol. 114, no. 21, pp. 9645–9650, 2010.
View at: Publisher Site | Google Scholar
N. Kanetake and M. Kobashi, “Innovative processing of porous and cellular materials by chemical reaction,” Scripta Materialia, vol. 54, no. 4, pp. 521–525, 2006.
View at: Publisher Site | Google Scholar
Y.-S. Hu, Y.-G. Guo, W. Sigle, S. Hore, P. Balaya, and J. Maier, “Electrochemical lithiation synthesis of nanoporous materials with superior catalytic and capacitive activity,” Nature Materials, vol. 5, no. 9, pp. 713–717, 2006.
View at: Publisher Site | Google Scholar
G. X. Pan, X. Xia, F. Cao, P. S. Tang, and H. F. Chen, “Porous Co(OH)₂/Ni composite nanoflake array for high performance supercapacitors,” Electrochimica Acta, vol. 63, pp. 335–340, 2012.
View at: Publisher Site | Google Scholar
Y. Guo, H. Yui, H. Minamikawa et al., “Dimension control of glycolipid nanotubes by successive use of vesicle extrusion and porous template,” Chemistry of Materials, vol. 18, no. 6, pp. 1577–1580, 2006.
View at: Publisher Site | Google Scholar
I. Kazeminezhad, A. C. Barnes, J. D. Holbrey, K. R. Seddon, and W. Schwarzacher, “Templated electrodeposition of silver nanowires in a nanoporous polycarbonate membrane from a nonaqueous ionic liquid electrolyte,” Applied Physics A: Materials Science and Processing, vol. 86, no. 3, pp. 373–375, 2007.
View at: Publisher Site | Google Scholar
J. H. Yuan, F. Y. He, D. C. Sun, and X. H. Xia, “A simple method for preparation of through-hole porous anodic alumina membrane,” Chemistry of Materials, vol. 16, no. 10, pp. 1841–1844, 2004.
View at: Publisher Site | Google Scholar
W. Chen, J.-H. Yuan, and X.-H. Xia, “Characterization and manipulation of the electroosmotic flow in porous anodic alumina membranes,” Analytical Chemistry, vol. 77, no. 24, pp. 8102–8108, 2005.
View at: Publisher Site | Google Scholar
F. C. Meldrum and R. Seshadri, “Porous gold structures through templating by echinoid skeletal plates,” Chemical Communications, no. 1, pp. 29–30, 2000.
View at: Google Scholar
D. D. Krassimir, D. S. Valkovska, and P. A. Kralchevsky, “Hydrodynamic instability and coalescence in trains of emulsion drops or gas bubbles moving through a narrow capillary,” Journal of Colloid and Interface Science, vol. 267, no. 1, pp. 243–258, 2003.
View at: Google Scholar
R. Šimpraga, G. Tremiliosi-Filho, S. Y. Qian, and B. E. Conway, “In situ determination of the “real area factor” in H₂ evolution electrocatalysis at porous Ni-Fe composite electrodes,” Journal of Electroanalytical Chemistry, vol. 424, no. 1-2, pp. 141–151, 1997.
View at: Google Scholar
S. Rausch and H. Wendt, “Morphology and utilization of smooth hydrogen-evolving raney nickel cathode coatings and porous sintered-nickel cathodes,” Journal of the Electrochemical Society, vol. 143, no. 9, pp. 2852–2862, 1996.
View at: Google Scholar
I. J. Brown and S. Sotiropoulos, “Electrodeposition of Ni from a high internal phase emulsion (HIPE) template,” Electrochimica Acta, vol. 46, no. 17, pp. 2711–2720, 2001.
View at: Publisher Site | Google Scholar
Y. F. Yuan, X. H. Xia, J. B. Wu, J. L. Yang, Y. B. Chen, and S. Y. Guo, “Nickel foam-supported porous Ni(OH)₂/NiOOH composite film as advanced pseudocapacitor material,” Electrochimica Acta, vol. 56, no. 6, pp. 2627–2632, 2011.
View at: Publisher Site | Google Scholar
W. S. W. Ngah and M. A. K. M. Hanafiah, “Biosorption of copper ions from dilute aqueous solutions on base treatedrubber (Hevea brasiliensis) leaves powder: kinetics, isotherm, and biosorption mechanisms,” Journal of Environmental Sciences, vol. 20, no. 10, pp. 1168–1176, 2008.
View at: Publisher Site | Google Scholar
N. Zhang, H. Qiu, Y. Si, W. Wang, and J. Gao, “Fabrication of highly porous biodegradable monoliths strengthened by graphene oxide and their adsorption of metal ions,” Carbon, vol. 49, no. 3, pp. 827–837, 2011.
View at: Publisher Site | Google Scholar
S. Babel and T. A. Kurniawan, “Low-cost adsorbents for heavy metals uptake from contaminated water: a review,” Journal of Hazardous Materials, vol. 97, no. 1–3, pp. 219–243, 2003.
View at: Google Scholar
L. Wang and R.-H. Yoon, “Role of hydrophobic force in the thinning of foam films containing a nonionic surfactant,” Colloids and Surfaces A: Physicochemical and Engineering Aspects, vol. 282-283, pp. 84–91, 2006.
View at: Publisher Site | Google Scholar
F. Melo and J. S. Laskowski, “Fundamental properties of flotation frothers and their effect on flotation,” Minerals Engineering, vol. 19, no. 6-8, pp. 766–773, 2006.
View at: Publisher Site | Google Scholar
X. S. Dong, J. Q. Jiang, and T. Tian, “Effect of process parameters on specific surface area of porous nickel film obtained by electrodeposition with hydrogen bubbles as template,” Electroplating & Finishing, vol. 30, no. 2, pp. 1–3, 2011.
View at: Google Scholar
I. S. I. Adam and A. N. Anthemidis, “Flow injection wetting-film extraction system for flame atomic absorption spectrometric determination of cadmium in environmental waters,” Talanta, vol. 77, no. 3, pp. 1160–1164, 2009.
View at: Publisher Site | Google Scholar
L. Huang, H.-B. Wei, F.-S. Ke, X.-Y. Fan, J.-T. Li, and S.-G. Sun, “Electrodeposition and lithium storage performance of three-dimensional porous reticular Sn-Ni alloy electrodes,” Electrochimica Acta, vol. 54, no. 10, pp. 2693–2698, 2009.
View at: Publisher Site | Google Scholar
H. J. Sun, H. B. Jiang, S. H. Li et al., “Effect of alcohols as additives on the performance of a nano-sized Ru-Zn(2.8%) catalyst for selective hydrogenation of benzene to cyclohexene,” Chemical Engineering Journal, vol. 218, pp. 415–424, 2003.
View at: Google Scholar
J. S. Bernardes, J. Norrman, L. Piculell, and W. Loh, “Complex polyion-surfactant ion salts in equilibrium with water: changing aggregate shape and size by adding oil,” Journal of Physical Chemistry B, vol. 110, no. 46, pp. 23433–23442, 2006.
View at: Publisher Site | Google Scholar
Y. Xiong and Y. Xia, “Shape-controlled synthesis of metal nanostructures: the case of palladium,” Advanced Materials, vol. 19, no. 20, pp. 3385–3391, 2007.
View at: Publisher Site | Google Scholar

Copyright

Copyright © 2014 Xiaogang Guo et al. This is an open access article distributed under the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.

PDF Download Citation

Download other formats

Order printed copies

Views

1740

Downloads

1601

Citations

Journal of Nanomaterials

Nanomaterials for Environmental Applications

Effects of Surfactants on High Regularity of 3D Porous Nickel for Zn2+ Adsorption Application

Abstract

1. Introduction

2. Materials and Methods

2.1. Materials and Reagents

2.2. Electrode Preparation

2.3. Electrolyte and Operating Conditions Preparation

2.4. Porosity and Surface Area Measurements

2.4.1. Porosity Measurements

2.4.2. Surface Area Measurements

2.4.3. Environmental Applications of 3D-PN Film

2.4.4. SEM, XRD, and AAS Measurements

3. Results and Discussion

3.1. Effect of the PEG 10000

3.2. Effect of the 1,4-Butynediol

3.3. Synergy Effect of PEG 10000 and 1,4-Butynediol

3.4. Adsorption Behavior of PN Film for Simulated Wastewater (Zn2+)

4. Conclusions

Conflict of Interests

Acknowledgments

References

Copyright

Effects of Surfactants on High Regularity of 3D Porous Nickel for Zn²⁺ Adsorption Application

3.4. Adsorption Behavior of PN Film for Simulated Wastewater (Zn²⁺)