Research article
Recycling of Pd(0) catalysts by magnetic nanocomposites—microbial extracellular polymeric substances@Fe3O4

https://doi.org/10.1016/j.jenvman.2020.111834Get rights and content

Highlights

  • Recycled Pd showed great catalytic reduction capacity to MB.

  • EPS from Klebsiella pneumoniae J1 showed superior Pd(II) adsorption capacity.

  • EPS@Fe3O4 showed superior adsorption capacity and high separation efficiency.

Abstract

Palladium (Pd) is extremely expensive due to its scarcity and excellent catalytic performance. Thus, the recovery of Pd has become increasingly important. Herein, microbial extracellular polymeric substances (EPS) and magnetic nanocomposite EPS@Fe3O4 were applied to recover Pd catalysts from Pd(II) wastewater. Results indicated that Pd(II) was reduced to Pd (0), which was then adsorbed by EPS (101.21 mg/g) and EPS@Fe3O4 (126.30 mg/(g EPS)). After adsorbing Pd, EPS@Fe3O4 could be collected by magnetic separation. The recovered Pd showed excellent catalytic activity in the reduction of methylene blue (MB). The pseudo-second-order kinetic model and Redlich-Peterson model best fit the adsorption results. According to spectral analysis, Pd(II) was reduced to Pd (0) by chemical groups in EPS and EPS@Fe3O4, and the hydroxyl had a chelating effect on adsorbed Pd. Therefore, EPS@Fe3O4 is an efficient adsorbent for recovering Pd from Pd(II) wastewater.

Introduction

Palladium (Pd), belonging to the precious platinum-group metals, has been widely applied in catalysis and other industries such as electroplating and precision manufacturing due to its high effectiveness and good stability (An et al., 2017; Le and Nishimura 2019; Yao et al., 2019). For example, Pd has been suggested to be an efficient catalyst for the reduction of toxic dyes to nontoxic or less toxic compounds (e.g., methylene blue (MB) to leuco-methylene blue (LMB)) (Hashemi Salehi et al., 2019; Ncube et al., 2015; Nguyen et al., 2018). However, Pd is expensive and extremely rare due to its excellent catalytic performance and its extremely scarce reserves (much less than gold) (Sharma and Rajesh 2016; Won and Yun 2013). The increasing demand for Pd has motivated the search for efficient methods to effectively recover and recycle Pd (Kim et al., 2017; Pat-Espadas et al., 2016; Wang et al., 2017).

Compared to conventional chemical materials, biological materials are renewable and do not introduce contamination (Beidokhti et al., 2019; Kim et al., 2020; Volesky 2007). A variety of microorganisms have been shown to be able to use enzymes to reduce soluble Pd(II) to insoluble Pd (0), thereby allowing the recovery of Pd from Pd(II) wastewater (Cui et al., 2017; Yates et al., 2013; You et al., 2019). However, considering appropriate temperature, oxygen, and nutriment requirements for microorganisms (Cordier et al., 2020; Jaroo et al., 2019), the recovery of Pd by microorganisms is to some extent restricted by the living conditions of microorganisms (Deplanche et al., 2014; Pat-Espadas et al., 2014).

Microbial extracellular polymeric substances (EPS) are mixtures extracted from microorganisms that mainly compose of proteins, polysaccharides and humic acids (Felz et al., 2019; Yan et al., 2019). EPS contains a wealth of functional groups (e.g., hydroxyl, carboxyl, and amino groups) that can adsorb metals through electrostatic interaction or complexation (Lai et al., 2018a; Palanivel et al., 2020; Yan et al., 2017). Moreover, EPS has been proven to demonstrate reducibility toward precious metals, such as Ag (Wei et al., 2017; Zhang et al., 2016). Compared with organisms, the resiliency of EPS compared to organisms allows for their continued function in some unforgiving conditions. Therefore, EPS could offer golden opportunities for the reduction and sequential adsorption of Pd(II) from Pd(II) wastewater, even though the mechanism of reduction and adsorption of Pd(II) by EPS has not been verified.

To the best of our knowledge, most research on Pd(II) recovery has focused on the adsorption of Pd but has ignored the collection and reuse of Pd (Chen et al., 2019; Zhou et al., 2016b). The separation and collection of Pd is difficult and time-consuming when the adsorbents are hard to separate from water. Magnetic separation technology has been increasingly studied for its convenient separation property (Theingi et al., 2019; Wei et al., 2017; Yang et al., 2020). In our previous work, EPS has been successfully combined with magnetic nanopowders, and a synthetic material EPS@Fe3O4 has been successfully used to reduce and adsorb Ag+ (Wei et al., 2017). Compared to common precious metals such as Ag+, the ionic forms of Pd(II) which play a significant role in Pd(II) recovery are more complicated. There are various of ionic forms of Pd(II) (e.g., PdCl42−, PdCl3, Pd(OH)+) and ion distribution of Pd(II) is dependent on pH conditions (Zhou et al., 2016a). The ionic forms of Pd(II) are important in its adsorption process. Therefore, further research on the recovery of Pd(II) based on its ionic forms is needed.

Furthermore, collecting Pd is not enough for reusing Pd because the recovered Pd may not function normally as a catalyst. The catalytic activity of Pd catalysts highly depend on their size, morphology and composition, therefore there are numerous studies on the synthesis of Pd catalysts (Hu et al., 2019; Wu et al., 2019; Zhang et al., 2020). However, most researchers who have studied the recovery of Pd rarely conduct a further investigation on the reuse of recovered Pd (Pat-Espadas et al., 2016; Zhou et al., 2016b). Therefore, the catalytic activity of recovered Pd also needs to be investigated after Pd is collected from Pd(II) wastewater. Among the numerous targeted contaminants of Pd catalysts, methylene blue (MB) is a model dye contaminant that is difficult to degrade but can be reduced to leuco-methylene blue (LMB) in the presence of a Pd catalyst (Hashemi Salehi et al., 2019; Nguyen et al., 2018).

In this work, EPS and a magnetic nanocomposite EPS@Fe3O4 were applied to recover and collect Pd catalysts from Pd(II) wastewater. The relationship between the Pd(II) ionic forms and the zeta potential of these two adsorbents were investigated. Reduction and adsorption mechanisms were investigated (adsorption kinetics, isotherms, and participating functional groups in the two adsorbents). The catalytic performance of the recovered Pd was tested by observing the reduction of methylene blue. This work is significant in regard to the recycling of Pd and other precious platinum-group metals.

Section snippets

Materials and methods

The research methodology of this study is shown in Fig. 1.

Impacts of the initial solution pH

The pH is crucial in the adsorption process because major factors (e.g., zeta potential of adsorbent and the ion forms) that can influence adsorption capacity are determined by pH (Zhou et al., 2020). The Pd(II) adsorption capacity and zeta potential of EPS and EPS@Fe3O4 at different pH values are displayed in Fig. 2(a)~ (b). The two adsorbents both performed best at pH = 5, and the adsorption capacity decreased as pH decreased. All of the other adsorption experiments in this study were carried

Conclusions

EPS and magnetic EPS@Fe3O4 were applied to effectively recover Pd from Pd(II) wastewater. Pd(II) was reduced to Pd (0) by EPS and EPS@Fe3O4 and then Pd was adsorbed. The magnetic EPS@Fe3O4 showed greater maximum adsorption than EPS and realized easy magnetic separation after adsorption. The reclaimed Pd showed excellent catalytic activity in the reduction of MB, suggesting the promising prospects of EPS@Fe3O4 in the recycling of Pd catalyst from Pd(II) wastewater. In future work, more catalytic

Credit author statement

Lu Zhou: Conceptualization, Formal analysis, Writing – original draft. Jixian Yang: Supervision, Funding acquisition. Fang Ma: Supervision, Funding acquisition. Shanshan Pi: Resources, Investigation. Aiqi Tang: Resources, Investigation. Ang Li: Supervision, Funding acquisition, Project administration, Writing – review & editing.

Declaration of competing interest

The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.

Acknowledgements

This work was financially supported by the National Natural Science Foundation of China [No. 51578179] and the Open Project of State Key Laboratory of Urban Water Resource and Environment, Harbin Institute of Technology [No. ES201807].

References (43)

  • S. Sharma et al.

    Augmenting the adsorption of palladium from spent catalyst using a thiazole ligand tethered on an amine functionalized polymeric resin

    Chem. Eng. J.

    (2016)
  • B. Volesky

    Biosorption and me

    Water Res.

    (2007)
  • S. Wang et al.

    Innovative conditioning of algal-based sorbents: macro-porous discs for palladium sorption

    Chem. Eng. J.

    (2017)
  • S.W. Won et al.

    Recovery of metallic palladium from hydrochloric acid solutions by a combined method of adsorption and incineration

    Chem. Eng. J.

    (2013)
  • P. Yan et al.

    Thermodynamics of binding interactions between extracellular polymeric substances and heavy metals by isothermal titration microcalorimetry

    Bioresour. Technol.

    (2017)
  • Z.R. Yan et al.

    Insights into the interactions between triclosan (TCS) and extracellular polymeric substance (EPS) of activated sludge

    J. Environ. Manag.

    (2019)
  • J. Yang et al.

    Magnetic nanocomposite microbial extracellular polymeric substances@Fe3O4 supported nZVI for Sb(V) reduction and adsorption under aerobic and anaerobic conditions

    Environ. Res.

    (2020)
  • C. Yao et al.

    Low cost and rapid fabrication of copper sulfides nanoparticles for selective and efficient capture of noble metal ions

    Chem. Eng. J.

    (2019)
  • L.X. You et al.

    Extracellular electron transfer of Enterobacter cloacae SgZ-5T via bi-mediators for the biorecovery of palladium as nanorods

    Environ. Int.

    (2019)
  • X. Zhang et al.

    Light-induced reduction of silver ions to silver nanoparticles in aquatic environments by microbial extracellular polymeric substances (EPS)

    Water Res.

    (2016)
  • L. Zhou et al.

    Combining high electron transfer efficiency and oxidation resistance in nZVI with coatings of microbial extracellular polymeric substances to enhance Sb(V) reduction and adsorption

    Chem. Eng. J.

    (2020)
  • Cited by (8)

    • Covering extracellular polymeric substances to enhance the reactivity of sulfidated nanoscale zerovalent iron toward Cr(VI) removal

      2022, Chemical Engineering Journal
      Citation Excerpt :

      Unlike those abiotic materials, extracellular polymeric substances (EPS) are promising biological agents as non-toxic, biodegradable, and economical macromolecular biochemicals metabolically secreted by microorganisms [12,13]. EPS have been applied to improve other iron-based nanomaterials, such as nZVI and Fe3O4, and have successfully combined the respective advantages of iron-based materials and EPS, with promising results in removing Ag(I), Pd(II), and Sb(V) [14–16]. However, the modification of sulfidated nanoscale zerovalent iron (SnZVI) by EPS is a subject that remains unstudied.

    • Sustainable and efficient technologies for removal and recovery of toxic and valuable metals from wastewater: Recent progress, challenges, and future perspectives

      2022, Chemosphere
      Citation Excerpt :

      Subsequently, the formed iturin-Ag NPs were easily and efficiently recovered from the complex reaction mixtures using an electro-precipitation process (Zhao et al., 2020e). Furthermore, EPSs have also shown excellent performance in reducing several metals from aqueous media, including Ag (Wei et al., 2018), Pd (Zhou et al., 2021), Cu (Xu et al., 2021c), and Sb (Yang et al., 2020b; Zhou et al., 2019b, 2020c). Similar to metals bio-reduction, oxidation of metal pollutants was also achieved using metal-oxidizing microorganisms, mainly targeting As (Dey et al., 2016; Huang et al., 2019e; Kumari et al., 2019; Sher et al., 2021; Sher and Rehman, 2019; Singh et al., 2021c; Wu et al., 2021e).

    • Effective adsorption of methylene blue dye from water solution using renewable natural hydrogel bionanocomposite based on tragacanth gum: Linear-nonlinear calculations

      2021, International Journal of Biological Macromolecules
      Citation Excerpt :

      Thus, water treatment and removal of this dye is an essential task that the industry should do with the cooperation of the academic society. Different studies were done to remove MBD, and several procedures have been utilized to remove dyes from wastewater [13–18]. Still, they need too much energy, while the adsorption does not, due to the low cost, high effectiveness, simplicity, and ease of design [19–23].

    View all citing articles on Scopus
    View full text