Obida
Bawadkji
a,
Peng
Tang
a,
Christian
Müller
*b and
Rainer
Haag
*a
aInstitut für Chemie und Biochemie, Freie Universität Berlin, Takustr. 3, 14195 Berlin, Germany. E-mail: haag@zedat.fu-berlin.de
bInstitut für Chemie und Biochemie, Freie Universität Berlin, Fabeckstr. 34/36, 14195 Berlin, Germany. E-mail: c.mueller@fu-berlin.de
First published on 27th May 2025
Rapid and sustainable methods for precious metal recovery are urgently needed to support circular economy initiatives. Herein, we introduce a one-pot mechanochemical route to synthesize a black phosphorus–polyglycerol (BP–PG) nanohybrid with enhanced interfacial reactivity for selective gold ion reduction. The process transforms inexpensive red phosphorus directly into amorphous BP and, subsequently, into BP–PG via planetary ball milling, thereby eliminating high temperatures, extended reaction times, and toxic solvents commonly used in conventional functionalized-BP nanomaterial syntheses. This “grafting-from” polymerization of glycidol onto BP yields a uniform, hydrophilic hybrid that can rapidly and selectively reduce gold ions to stabilized gold nanoparticles. Notably, BP–PG recovers more than three times its own weight in gold, far surpassing previously reported materials, while leveraging a scalable, cost-effective, and green production method. These findings underscore the critical role of synthetic strategy and material architecture in achieving high-performance nanohybrids, offering promising opportunities for precious metal recovery and broader interface-driven applications.
Green foundation1. We developed a solvent-free, mechanochemical route to synthesize a black phosphorus–polyglycerol nanohybrid, effectively eliminating harmful solvents and reducing energy use and reaction times, for the recovery of gold from e-waste. This method aligns with green chemistry principles by promoting resource recovery while minimizing environmental impact through selective recovery of precious metals.2. Our key achievement is a one-pot synthesis that circumvents toxic solvents, requires no high-temperature chemical vapor transport, and achieves remarkable gold uptake, exceeding three times the material's weight. The resulting biodegradable nanohybrid prevents long-term ecological harm. 3. Future efforts could focus on scaling up ball-milling process and adopting bio-based glycidol sources. Although mechanochemistry offers scalability potential, further research could explore optimizing the mechanochemical process to enhance throughput. Moreover, investigating the use of bio-derived precursors for glycidol could improve the sustainability of the starting materials. |
Black phosphorus (BP) nanomaterials provide a sustainable and efficient solution for recovering and reducing gold ions due to their high surface area and abundant active sites for metal ion adsorption.13–17 Phosphorus atoms in BP reduce gold ions (Au3+) to elemental gold (Au0) under mild conditions without external reducing agents, leading to the spontaneous formation of gold nanoparticles on BP nanosheets.14,15 This dual functionality simplifies the recovery process and reduces chemical consumption, making it environmentally friendly and cost-efficient.15 BP is also biodegradable, degrading into benign phosphates,18,19 and it exhibits high selectivity for gold ions over other metals.14,15 Zhang et al. functionalized black phosphorus with poly(N-isopropylacrylamide) (PNIPAM) to create a responsive material (BP–P) that enables rapid, highly selective extraction of precious metals like gold, silver, and palladium under mild conditions, with potential applications in hydrogen evolution reactions.15,20
However, current methods for producing BP nanomaterials face significant limitations such as high cost, complexity, toxicity, and lack of scalability. Typically, BP nanomaterials are derived from liquid exfoliation of BP crystals produced via the expensive, toxic, and non-scalable chemical vapor transport (CVT) method, which utilizes heavy-metal iodides, costs 570–700 € per g and requires over 18 hours to complete.21–23 Producing and functionalizing BP nanomaterials involves further steps like mechanical crushing and ultrasonication in toxic solvents, use of hazardous activating agents, and requires costly purification procedures.24–26 Alternative solvothermal techniques have been developed but are also economically and ecologically non-feasible due to the use of toxic materials and are suitable only for obtaining small amounts of BP.27,28 Additionally, pure BP nanomaterials aggregate in aqueous solutions,29 so they require covalent functionalization with hydrophilic materials like polyglycerol (PG).26,30,31 However, polymer functionalization is typically achieved through challenging, costly, and often toxic solvent-based methods.15,26,31 These processes encapsulate the nanomaterial, limiting its interaction with surroundings and reducing performance in interfacial applications.18,26,32 Exfoliating expensive BP crystals using techniques like sonication yields low amounts of few-layered nanosheets with minimal defects and pores, resulting in a lower surface area compared to amorphous structures.24,26 Gold nucleation on BP nanosheets primarily occurs at defects or edges, promoting the growth of gold nanoparticles.14,33 While BP nanosheets can be fixed onto solids with higher surface areas, such as covalent organic frameworks or porous spherical montmorillonite, this adds expense and complexity to the functionalization process.34,35
A more sustainable, green, and rapid method for producing functional BP nanomaterials is mechanochemistry.36,37 In the context of BP synthesis, mechanochemical methods enable the direct transformation of RP into BP under ambient conditions.38–46 eliminating the need for high temperatures, high pressures, toxic reagents, enhances energy efficiency, significantly reduces synthesis times, and allows better control over particle size and crystallinity, which is crucial for high-quality BP materials.38–40,46 Regarding BP nanomaterial production, mechanochemical processes under the right conditions can directly form nanomaterials without further processing, addressing challenges of traditional exfoliation techniques,46 as well as allowing subsequent surface functionalization to improve BP's dispersibility in aqueous solutions and stability under ambient conditions, enhancing its performance in various applications.32
Here, we introduce a solventless, mechanochemically synthesized black phosphorus–polyglycerol (BP–PG) nanohybrid as a high-capacity selective precious metal recovery agent (Fig. 1). This rapid, eco-friendly method aligns with green chemistry principles, and the biodegradability of black phosphorus ensures minimal environmental impact.47–49 This work pioneers the first successful mechanochemical polymerization of glycidol into polyglycerol using a “grafting-from” technique, representing an advancement in mechanochemical polymerizations as low-functional liquid epoxides do not polymerize so easily mechanochemically.50 Our approach creates a true nanohybrid by combining a solid inorganic nanomaterial (BP) with a liquid organic nanomaterial (PG) in a one-pot process starting from red phosphorus (RP) and glycidol, both relatively inexpensive starting materials.51,52 The resulting highly hydrophilic nanomaterial is ideal for aqueous environments. BP serves as an efficient gold-reducing agent, while PG functions as both a stabilizer for gold nanoparticles (AuNPs) and a hydrophilic component that ensures uniform distribution and prevents aggregation.53 Previous syntheses relied on toxic solvents and suffered from low yields and time-consuming purification.26 In contrast, our solventless approach retains both components’ properties, enabling selective recovery of gold ions under complex acidic conditions and directly producing mesodisperse stabilized AuNPs.
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Fig. 1 BP–PG as a recovery agent for Au from electronic waste, contributing to a circular economy. AI-generated nanomaterial image. |
Although mechanochemical methods have shown promise as a green and cost-effective route to black phosphorus, achieving consistently high-quality yields and large-scale production remains an active area of research.39,40,54 Therefore, obtaining sufficient amounts of high-quality BP within a reasonable processing time via a green, non-expensive and facile method is a key requirement for achieving realistic implementation of BP for different applications. To obtain high quality BP mechanochemically within a reasonable amount of time, a relatively high ball-to-powder ratio (BPR) of >25:
1 is necessary (Fig. 2b and ESI 1†). Depending on the available ball-mill apparatus, gram-scale yields of high-quality BP nanoparticles can be obtained within a few-hour of milling time (Fig. 2e). The Raman spectrum of the formed BP nanoparticles (mBP) using HEPBM shows a high allotropic conversion mainly seen by the pronounced generation of the B2g and the A2g black phosphorus vibrational peaks at 435 cm−1 and 463 cm−1, respectively, and the strong depletion of the broad band between 368–425 cm−1. Additionally, a blue shift of the B1 red phosphorus peak at 350 cm−1 to the A1g black phosphorus peak at ∼360 cm−1 (Fig. 2c and ESI 1†) can be observed, which closely resembles the vibrational bands of cBP obtained via CVT. Comparatively, these vibrational features from sBP are not clearly indicated even after heating at 170 °C. Raman maps obtained from mBP show a narrow distribution of the BP Raman vibrational bands (ESI 1†), which indicates an exceptional uniformity in quality. Moreover, dynamic light scattering spectroscopy (DLS) of an mBP dispersion (Fig. 2l) reveals nano-sized particles. We therefore anticipate that our suggested mechanochemical approach can produce high-quality mBP nanoparticles in a single step. Although the CVT method resulted in a high allotropic conversion for cBP, the solvent-based exfoliation did not produce BP nanoparticles with a uniform morphology, which can be concluded by the broader distribution of Raman vibrational bands in the acquired Raman map (Fig. 2c and ESI 1†). In such a procedure, it is typical to separate the bulky particles from the exfoliated nanoparticles via centrifugation, which leads to a high loss in BP yield.26 The Raman map from sBP reveals a low allotropic conversion, which can be attributed to the hindered access of the ethylenediamine solvent to the inner core of the RP particles throughout the synthesis, leading to an allotropic conversion mostly on the surface of the treated particles (Fig. 2c and ESI 1†). Likewise, 31P-MAS-NMR spectroscopy of sBP indicates a heterostructure of red and black phosphorus, whereas mBP shows a clear single broad signal at δ = ∼19.0 ppm, that indicates amorphous BP (Fig. 2d). The amorphous nanoparticle morphology of the produced mBP, which results from the process of HEPBM, is also obvious by the lack of diffraction pattern of BP, which are present in the layered crystal structure of cBP (ESI 1†). This amorphous morphology is desired for its application as a recovery agent, as the surface area is higher than that of few-layer BP nanosheets.
Considering the high quality of the produced BP nanoparticles, which were obtained in a quick, facile, and environmentally friendly approach, mBP was used for further functionalization with PG (Fig. 2a and b). The benefits of mechanochemically produced BP–PG were assessed in terms of synthesis, hybridity of properties, environmental-friendliness, production cost, and its ability to selectively recover gold in the form of AuNPs with a high recovery capacity from an ionic mixture of metals.
BP–PG was obtained via a HEPBM approach by combining a 1:
1 w/w ratio of mBP and glycidol in a stainless-steel chamber together with a stainless-steel ball-mill medium and treating both reagents at a high milling energy under inert atmosphere. Thus, BP–PG can be obtained in a one-pot two-step process starting from only RP and glycidol. On the other hand, BP@PG was obtained by adapting a similar procedure previously reported from our research group, but using the same produced mBP and mBP/glycidol w/w ratio of 1
:
1 for a comparative assessment.26 Both reagents were dispersed in NMP and treated at 120 °C for 72 hours under inert atmosphere before purification of the nanoparticles to finally obtain BP@PG. Regarding BP–PG, a successful polymerization of glycidol to PG and functionalization of the BP nanoparticles can occur within 15 minutes at high milling energies as seen by the development of the polyglycerol multiplet between δ = 3.4–4.0 ppm in the 1H-NMR spectra55 (Fig. 2g amd ESI 2b†), whereas only a weak signal appears for PG even after 72 hours of heating at high temperatures (ESI 2a†). 31P-MAS-NMR shows a sharp intense signal at δ = ∼0.0 ppm, that indicates P–O bonds arising from a high-degree functionalization of BP by glycidol monomers which polymerized onto BP nanoparticles (Fig. 2f). BP@PG, however, was functionalized to a much lesser degree as indicated by a very broad signal around δ = ∼0.0–10.0 ppm, which is typical for PxOy species (ESI 2c†). Fourier transform infrared spectroscopy (FT-IR) reveals intense signals for BP–PG at 1240 cm−1 and 978 cm−1, that corresponds to the P–O–C asymmetric and symmetric stretches, respectively, as well as all the characteristic PG stretches for the O–H, C–H, and C–O–C bonds at 3000–3600 cm−1, 2877 cm−1, and 1045 cm−1, respectively (Fig. 2h).55 These signals are not noticeable for BP@PG. Similarly, Raman vibrational bands for BP@PG are relatively attenuated in comparison to BP and BP–PG as seen by the broadness of the A1g, B2g, A2g peaks (ESI 2d†) because the polymer coverage scatters the incoming laser light and absorbs part of the scattered Raman light. The X-ray photoelectron spectroscopy (XPS) P2p spectrum shows P–P bonds from the BP component at 130–131 eV and P–O and P–C bonds from the BP–PG covalent functionalization at 134–135 eV (Fig. 2I and ESI 3†). The C1s spectrum (Fig. 2j and ESI 3†) indicates C–O bonds mainly from the PG component at 286 eV and C–P and O–C–O bonds from the BP–PG covalent functionalization at 284 eV and 287 eV, respectively. On the other hand, XPS analysis of BP@PG revealed functionalization to a lesser degree indicated by the smaller P–O and P–C peak in the P2p spectrum (ESI 3†), and a smaller C–O peak in the C1s spectrum. This is also indicated by the higher carbon-to-phosphorus atomic ratio derived from the survey spectra (ESI 3†) of BP–PG (∼4.72) as compared to that of BP@PG (0.32). Based on our results, we propose that the epoxide ring of glycidol undergoes nucleophilic ring-opening by the phosphorus atoms in BP, initially forming P–C bonds. Subsequently, the oxygen sites of the growing polyglycerol chains can further react with BP to establish additional P–O linkages, thereby building the integrated BP–PG network.
Varying the BP-to-glycidol weight ratio, especially by reducing it, in the mechanochemical process hindered successful polymerization into polyglycerol-functionalized BP nanoparticles (ESI 4a and c†). This likely resulted from insufficient BP substrate, as glycidol, a low-molecular-weight liquid epoxide, could require ample reactive surface sites, like those on BP, to initiate polymerization effectively. The resulting products were characterized by FTIR and 1H-NMR, revealing that sufficient BP surface is essential for an effective mechanochemical ring-opening of glycidol, which otherwise remains largely unpolymerized at high glycidol/bulk BP ratios. Conversely, a very high BP content can limit polyglycerol formation, affecting the final materials’ dispersibility and performance.
Regarding production time, the mechanochemical approach can be used for both a rapid allotropic conversion of BP and a high-degree functionalization with PG via anion ring opening polymerization of glycidol in a one-pot two-step process, standing out as the favorable approach in practical scenarios (Fig. 3). Attempting a single-step reaction between RP and glycidol lead to various chemical species different than that obtained by the 2-step approach that yields BP–PG (ESI 4b and d†), likely due to various side reactions between RP and glycidol that hinder the allotropic transformation of RP to BP and its functionalization with polyglycerol thereafter.
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Fig. 4 (a) Overall scheme of AuNP production and recovery from EWL treated with BP–PG. SEM images of (b) AuNP@BP–PG and (c) AuNPs recovered from BP–PG. (d) AAS analysis of metals present in solution after treatment with BP–PG indicating high selectivity for Au. (e) Work functions of the metals in EWL giving insight to the selective BP–PG/AuCl4− redox pair formation.63 (f) CV analysis of BP–PG showing irreversible oxidation of the nanomaterial. (g) UV-Vis and (h) Au 4f XPS analysis of the AuNPs formed from treatment of EWL with BP–PG, both indicating reduced zero-valent Au species. (i) Treatment of AuNP@BP–PG with H2O2 to oxidize the BP–PG component to finally recover the AuNPs. AI-generated nanomaterial image. |
BP–PG's selectivity towards metals most found in EWL was tested (Fig. 4d), specifically AuIII, FeIII, CuII, NiII, ZnII, and CrIII, in acidic solutions (pH 1.0) as commonly derived from electronic waste. To concentrated metal chloride and nitrate solutions (0.5 mg mL−1 of each), BP–PG was added (1 mg mL−1) and the mixtures were treated for 30 minutes before letting the nanoparticles sediment over 30 minutes, in which the supernatants were collected and analyzed by AAS. None of the metals apart from gold were reduced by BP–PG (Fig. 4d). To gain a mechanistic insight into the interaction between BP–PG and these metals, a cyclic voltammogram (CV) of a BP–PG dispersion was obtained (Fig. 4f) that reveals an irreversible oxidation of the phosphorus component from P0 to P3+ and P5+, which are finally converted to H3PO4, indicated by the peak at +630.4 mV vs. Ag/AgCl (or 835.4 vs. standard hydrogen electrode (SHE)).49,60–62 As the reduction potential of [AuCl4]− to zero-valent Au0 is +1002 mV vs. SHE, which is higher than the work function of BP–PG (+835.0 mV vs. SHE), an electron transfer from BP–PG to [AuCl4]− can occur spontaneously without the need of external energy/activation.14,15,59 On the other hand, all other metal ions have work functions lower than that of BP–PG (Fig. 4e).63 Therefore, an interaction between BP–PG and [AuCl4]− leads to the formation of the redox pair BP–PG/AuCl4−, where the BP–PG reduces the metal cation to the zero-valent state, thereby oxidizing the BP component of BP–PG. After treatment of EWL with BP–PG, the zero-valent gold is reduced onto BP–PG in the form of nanoparticles. The gold-loaded nanohybrid (AuNP@BP–PG, Fig. 4b and 5g) can sediment from the mixture within a short amount of time (<1 hour), which allows the transfer of the gold-free EWL to waste-water treatment. To recover the AuNPs from AuNP@BP–PG, the BP component can be oxidized to H3PO4. This can be done naturally under ambient conditions where the BP component is oxidized by oxygen or can be done on demand by using a stronger oxidizing agent such as hydrogen peroxide (Fig. 4i). In both cases, the degradation of the BP–PG nanoparticles will release the AuNPs to form a pink-red dispersion of gold nanoparticles (Fig. 4i and ESI 6†). SEM images show mesodisperse gold nanoparticles with a size of ∼50 nm (Fig. 4c, 5d and g). UV-Vis analysis of these dispersions reveals the characteristic absorbance of gold nanoparticles at ∼537 nm (Fig. 4g). High-resolution Au 4f XPS analysis indicates zero-valent Au0 species, proving the reduction of AuIII to AuNP, as well as a small portion of AuI species. Moreover, Cu 2p3/2 XPS analysis indicates adsorption of Cu ions onto the surface of BP–PG due to the known ability for copper-ions to interact with BP and oxidize it (ESI 5†), although only in negligible amounts as proven by AAS (Fig. 4d).64 SEM images of the AuNPs derived from mBP reveal a non-uniform morphology (Fig. 5g), which may be a result of the lack of a stabilizing agent such as PG (Fig. 5b). This implies that composition of BP–PG is favorable for the formation of spherical mesodisperse gold nanoparticles which could be stabilized by the polymeric PG component.
To validate this, the gold recovery capacity from EWL of mBP, cBP, BP–PG, BP@PG, BP + PG, and activated carbon (AC) was assessed (Fig. 5e). As mentioned earlier, mBP was used for the preparation of BP–PG, BP@PG, and BP + PG to achieve comparable results. Specifically, amorphous mBP was compared to its expensive crystalline counterpart cBP, and BP–PG was compared to its expensive solvent-derived counterpart BP@PG. This comparison aimed to evaluate the impact of the materials’ architectures on AuIII reduction. Both mechanochemically-derived BP–PG and mBP demonstrated the ability to reduce gold ions more than 3 times their weight—nearly triple the capacity of previously reported nanomaterials.15,68–73
A significant impact on the quality and the capacity of the produced Au0 species is determined by the architecture and distribution of the reducing-agent (BP) and nanoparticle stabilizing polymer (PG) of a recovery platform (Fig. 5a, d, g and ESI 7†). Studies have shown that dendritic polyglycerol (dPG) can be used to stabilize and functionalize AuNPs, that enhances their dispersibility and stability in aqueous environments. The hydrophilic nature of polyglycerol improves the uniform distribution of AuNPs, preventing aggregation.53 As the PG component in BP–PG is uniformly embedded within the BP component (Fig. 5a and g), mesodisperse AuNPs (<100 nm) are formed (Fig. 5d and g). On the other hand, the PG component in BP@PG is more separated by covering parts of the BP surface (Fig. 5a and g), that results in a lower Au recovery capacity (Fig. 5e). Also, with less PG in BP@PG (Fig. 2m), large polydisperse AuNPs are formed as shown in Fig. 5d and g. Without any PG to stabilize AuNPs in amorphous mBP, AuNPs with various morphologies are formed (Fig. 5g). Crystalline few-layered cBP nanoflakes produce less-desirable large non-dispersible bulk gold structures (Fig. 5g). The lower surface area attributed to a few-layer tightly stacked crystalline structure consequentially leads to a much lower recovery capacity by cBP (∼1/3) as compared to mBP and BP–PG (Fig. 5e). It is crucial to highlight that the amorphous structure of the BP component in mBP, BP–PG, BP@PG, and BP + PG, confirmed by solid-state NMR spectroscopy (Fig. 2d) and PXRD analysis (ESI 1†), contributes to an increased surface area compared to the reported exfoliated BP two-dimensional nanoflakes. Thus, mercury intrusion porosimetry (MIP) measurements reveal a three-fold increase in the total pore area, or specific surface area (SSA), after mechanochemical treatment to 8.4 m2 g−1 for mBP as compared to 2.7 m2 g−1 for its precursor, RP (Fig. 5c, f and ESI 9†). Such a substantial SSA is beneficial for applications that rely on surface interactions, such as ion-reduction, catalysis, adsorption, and sensor technologies, as a higher SSA means more surface area is available for these interactions.74,75 The increased porosity induced by HEPBM is advantageous for the nucleation and subsequent growth of gold nanoparticles (AuNPs), as these pores serve as primary seeding sites facilitating AuNP formation.14,33 Moreover, the average pore diameter for mBP was decreased down to 0.366 μm from 1.03 μm for its RP precursor (Fig. 5f and ESI 9†). These small nanosized pores are favorable for the reduction of AuIII to small and highly-desirable AuNPs, as shown in Fig. 5g. Finally, the superior dispersibility of BP–PG, also attributed to the hydrophilic nature of PG, ensures uniform nanomaterial distribution in aqueous environments. This contrasts sharply with mBP's tendency to agglomerate, that reduces its dispersibility and complicating its application by necessitating additional steps to disperse it in aqueous systems (Fig. 5b and ESI 8†).
AC | Activated carbon |
AAS | Atomic absorption spectroscopy |
AuNP | Gold nanoparticle |
AuNP@BP–PG | Gold-loaded black phosphorus–polyglycerol |
BP | Black phosphorus |
BP–PG | Black phosphorus–polyglycerol nanohybrid |
BP@PG | Solvent polyglycerol-functionalized BP nanoparticles |
BPR | Ball-to-powder ratio |
cBP | Crystalline black phosphorus (via CVT) |
CVT | Chemical vapor transport |
CV | Cyclic voltammetry |
DLS | Dynamic light scattering |
dPG | Dendritic polyglycerol |
EWL | Electronic waste leachate |
FT-IR | Fourier transform infrared spectroscopy |
(HE)PBM | (High-energy) planetary ball milling |
MIP | Mercury intrusion porosimetry |
mBP | Mechanochemically derived black phosphorus |
NMP | N-Methyl-2-pyrrolidone |
PG | Polyglycerol |
PXRD | Powder X-ray diffraction |
RP | Red phosphorus |
SEM | Scanning electron microscopy |
sBP | Solvothermally derived black phosphorus |
SSA | Specific surface area |
TGA | Thermogravimetric analysis |
XPS | X-ray photoelectron spectroscopy |
ZP | Zeta potential |
Footnote |
† Electronic supplementary information (ESI) available. See DOI: https://doi.org/10.1039/d5gc00274e |
This journal is © The Royal Society of Chemistry 2025 |