Xiaoteng
Jia
a,
Xuenan
Ma
a,
Li
Zhao
a,
Meiying
Xin
b,
Yulei
Hao
b,
Peng
Sun
a,
Chenguang
Wang
a,
Danming
Chao
d,
Fangmeng
Liu
*a,
Caiyun
Wang
*c,
Geyu
Lu
*ae and
Gordon
Wallace
c
aState Key Laboratory of Integrated Optoelectronics, College of Electronic Science and Engineering, Jilin University, Changchun 130012, China. E-mail: liufangmeng@jlu.edu.cn; lugy@jlu.edu.cn
bJilin Provincial Key Laboratory of Pediatric Neurology, Department of Pediatric Neurology, The First Hospital of Jilin University, 130021, China
cARC Centre of Excellence for Electromaterials Science, Intelligent Polymer Research Institute, AIIM Faculty, University of Wollongong, Wollongong, NSW 2522, Australia. E-mail: caiyun@uow.edu.au
dCollege of Chemistry, Jilin University, Changchun 130012, China
eInternational Center of Future Science, Jilin University, Changchun 130012, China
First published on 25th January 2023
Implanted rechargeable batteries that can provide energy over a sufficient lifetime and ultimately degrade into non-toxic byproducts are highly desirable. However, their advancement is significantly impeded by the limited toolbox of electrode materials with a known biodegradation profile and high cycling stability. Here we report biocompatible, erodible poly(3,4-ethylenedioxythiophene) (PEDOT) grafted with hydrolyzable carboxylic acid pendants. This molecular arrangement combines the pseudocapacitive charge storage from the conjugated backbones and dissolution via hydrolyzable side chains. It demonstrates complete erosion under aqueous conditions in a pH-dependent manner with a predetermined lifetime. The compact rechargeable Zn battery with a gel electrolyte offers a specific capacity of 31.8 mA h g−1 (57% of theoretical capacity) and outstanding cycling stability (78% capacity retention over 4000 cycles at 0.5 A g−1). Subcutaneous implantation of this Zn battery into Sprague-Dawley (SD) rats demonstrates complete biodegradation in vivo and biocompatibility. This molecular engineering strategy presents a viable avenue for developing implantable conducting polymers with a predetermined degradation profile and high energy storage capability.
Galvanic cells consisting of bioresorbable metals (e.g. Mg, Zn, Fe, Mo, and their alloys) have demonstrated utility in ingestible diagnostics.5,6 However, these primary batteries with short lifetimes (from hours to weeks) hinder the mid-term operation in vivo. Implanted rechargeable batteries that can sustain long-term cyclic use are preferred. Biologically derived redox-active biopolymers, such as melanin pigments, dopamine, and nicotinamide adenine dinucleotide cofactor, can be recharged in vivo.7,8 However, the lack of precise control over the biodegradation kinetics of these endogenous redox organics stemming from the complicated molecular structures may lead to undesirable biological responses. An inorganic intercalation material is also challenging in this case due to inferior electronic conductivity and sluggish ionic diffusion, leading to unfavorable rate capability and cycling stability.9 Therefore, alternative approaches are necessary to expand the toolbox for biocompatible energy storage materials with both desired electrochemical properties (e.g. high energy density, rate capacity, and cycling stability) and programmable biodegradable profiles under physiological conditions.10
Conducting polymers have demonstrated applicability as high-rate electrode materials attributed to pseudocapacitive-dominant energy storage behavior. They offer tunable charge storage, electronic, and degradation properties through molecular design.11 However, imparting both full biodegradation and electroactivity to conducting polymers represents a formidable challenge because of the limited cleavable linkages that could maintain extended conjugation along the backbone.12 The formed polymer composite from blending or covalent bonding with biodegradable polyesters, polyamides, and polyanhydrides13 can only be disintegrated leaving the active components in the body. These materials can only be disintegrated without complete chemical breakdown, leaving the active components in the body. To eliminate the undesired immune response caused by the undegraded active components, Bao and coworkers designed fully biodegradable semiconducting polymers for transient electronics by incorporating a reversible acid-labile imine bond into a diketopyrrolopyrrole-based polymer, where imine hydrolysis resulted in the cleavage of the polymer backbone.14,15 They further investigated the impact of side chains on the degradation lifetimes in different solvents.16 However, the hydrolytic cleavage chemistry along the polymer mainchain represents a particular challenge in maintaining the conjugation length, i.e. energy storage capacity. Moreover, the low electrical conductivity of these conjugated polymers significantly limits the practical application in batteries, where fast rechargeability and high cycling stability are highly desirable. A rationally tailored biodegradable conducting polymer with full biodegradation and high cycling stability is urgently needed to realize biodegradable rechargeable batteries.
Here, we present a biocompatible, fully erodible PEDOT derivative by adopting bio-resorption chemistry (Fig. 1) via both chemical and electrochemical routes. Covalent tethering of PEDOT with sulfonate and carboxyl groups endows the polymer with water solubility and wet-processing capability.17 To control the bioerosion rate, an ether spacer was linked to the acid group to decrease water solubility.18 Compared with the hydrolytically cleavable linkages at the polymer mainchain, side-chain engineering of ionizable and/or hydrolyzable carboxylic acid pendants concurrently allows for charge storage and modulation of dissolution kinetics without compromising electronic properties.19 The electropolymerized film, eliminating the need for conductive additives, delivers a high capacity, outstanding rate, and cycling performance when coupled with a Zn anode. This battery demonstrates complete disappearance in vivo through a series of metabolic and hydrolytic reactions, and its biocompatibility is evidenced by live–dead cell imaging and histological analysis. This work provides a new avenue for molecular engineering of biocompatible and fully erodible conducting polymers for an onboard energy supply.
To quantitatively analyze the bioerosion profile, we incubated the pellets of chemically polymerized PEDOT–COOH (30 mg, 10 mm diameter and 0.5 mm thickness) in buffers of varying pH. The solution was changed every 12 h and monitored using UV-Vis spectroscopy. The erosion rate was dramatically enhanced as pH increased with complete dissolution after 7 days at pH 7.4 and 4 days at pH 10 (Fig. 2a). This erosion rate was much higher than previously reported for bio-erodible polypyrrole (PPy) with the carboxylic acid group (27% weight loss after 80 days of incubation in pH 7.2 buffer) attributed to the hydrophilicity and polarity of ether side-chains.22 However, the weight loss was only 16% after 7 days of incubation in pH 4 buffer due to the inhibition of carboxyl hydrolysis under acidic conditions. The mass loss results coincided with the increased absorption at λ = 350 nm in the PBS solution (Fig. 2b). The main absorption peak at 350 nm associated with the presence of aromatic rings (PEDOT) gradually increased until 84 h, indicating an accelerated erosion process (Fig. 2c). The eroded product displayed the same absorption curve as pristine PEDOT–COOH in DMSO (Fig. S4†), confirming that the polymer was dissolving into the buffer solution.
To further understand the bioerosion process, we characterized the erosion products in PBS. We first collected and analyzed the solution using FTIR spectroscopy (Fig. S5†). A stretching vibration band around 3350–3500 cm−1 assigned to –OH was observed for the pristine polymer. With an increase in incubation time, the eroded products exhibited characteristic bands of the PEDOT backbone at 1184 cm−1 and 1517 cm−1 (C–O and CC), and a carboxyl group at 1705 cm−1 (–CO) with decreased signals for –OH. The almost identical FTIR curves revealed that the eroded product was generated by the dissolving polymer. The change in the surface morphology of PEDOT–COOH residual pellets was investigated by SEM (Fig. 2c). The pellet surface was even and uniform prior to incubation. After 3 days of erosion, the pellet experienced substantial weight loss, resulting in cracks. Several cavities were observed after 5 days due to the severe delamination of PEDOT–COOH particles. These results verify that surface erosion mediated the overall degradation of the PEDOT–COOH pellet.
Cytocompatibility is a prerequisite for biodegradable batteries. After confirming that the eroded products comprised PEDOT–COOH polymeric chains, we first assessed the cytotoxicity of eroded solutions at various concentrations to human adipose-derived stem cells (hADSCs) using 3-[4,5-dimethylthiazol-2-yl]-2,5 diphenyl tetrazolium bromide (MTT) assay. It is noted that a trace amount (<60 μg mL−1) of eroded solutions could promote cell growth (Fig. 2d). Although the cell viability dropped as the concentration of eroded solution increased, overall cell viability was always greater than 80% over a three day incubation, indicating the low cytotoxicity of eroded products.
We further assessed the suitability of the polymer films as substrates for cell adhesion by cultivating hADSCs on a PEDOT–COOH film with a PVA–Au substrate as the control. As the optical density (OD) value is directly proportional to the number of cells, and the OD value would represent the cell number. The cell proliferation increased as the time elapsed for both samples (Fig. 2e). The cell growth trend of PEDOT–COOH was similar to that of the control over 5 days of incubation, with no statistical difference in cell numbers as evidenced by the similar OD values. Calcein-AM and propidium iodide staining indicated high cell viability in those samples (Fig. 2f). hADSCs spread well and displayed a regular spindle shape and demonstrated good cell proliferation with much higher cell confluency during the three day culture. It is probably attributed to the hydrophilic nature of PEDOT–COOH, providing an adequate surface for cell adhesion.
Taken together, the cell proliferation and minimal cytotoxicity of both the polymer film and eroded products confirmed the compatibility of the PEDOT–COOH substrate.
The effect of bioerosion on the electrical and electrochemical properties was monitored during the incubation period in PBS solution. The electrical conductivity of the pristine PEDOT–COOH thin film on ITO was 1.8 S cm−1 measured by a four-point probe method (Fig. 2g). This conductivity was on par with literature values for β-substituted PEDOT.23 Due to the surface roughness caused by the erosion, we only monitored the sheet resistance during incubation in PBS. The sheet resistance (1800 ± 80 Ω) increased slightly and reached a plateau of 2530 ± 260 Ω after 5 days. This equilibrated resistance was similar to that of previously reported functionalized PEDOT used to stimulate cells and tissues in cell culture media.24
The cyclic voltammograms (CV) of the PEDOT–COOH film on ITO demonstrated a quasi-rectangular shape without a prominent redox peak in PBS solution (Fig. 2h), indicating high pseudocapacitive activity. Throughout the incubation period, CV profiles were maintained but with a smaller current response. After five days of incubation, a 73% decrease in the specific areal capacitance (9.2 mF cm−2) was observed (Fig. 2i), while the weight loss was 79% at this stage. The decrease in electrochemical activity may be attributed to the disruption of the continuous conductive PEDOT framework caused by surface erosion. The PEDOT–COOH film could maintain electrical and electrochemical activity during erosion under aqueous conditions. Then, after it has fulfilled the function, faster erosion induces rapid mass loss, leading to functional failure.
Galvanostatic charge–discharge (GCD) profiles demonstrated an almost symmetric and linear shape, implying a small intrinsic series resistance and fast charge–discharge process. The Zn battery delivered a specific capacity of 31.8 to 16.4 mA h g−1 at discharge densities from 0.25 to 10 A g−1 (Fig. 3d). The specific capacity of PEDOT–COOH at 0.25 A g−1 was 57% of its theoretical capacity (55.3 mA h g−1 based on a doping level of 0.5 electrons per monomer unit). Attributed to the pseudocapacitance-controlled process of the PEDOT–COOH cathode, the battery exhibited an excellent capacity retention rate (51.5%) at a high 10 A g−1 (Fig. 3e). When the current density was reverted to 0.25 A g−1, the initial capacity was nearly restored, demonstrating excellent reversibility. The pseudocapacitance from the conducting polymer backbone endowed the cathode with fast kinetics. Moreover, 78% of the capacity was retained after 4000 cycles at 0.5 A g−1, with a high coulombic efficiency of ∼98% (Fig. 3f). The surface morphology of the Zn anode was observed by using a scanning electron microscope (SEM). After long-term cycling, the surface was dense and flat without sharp dendrites (Fig. S8†), indicating the good stability of the Zn anode interfaced with the gel electrolyte.27 The Zn battery delivered a maximum areal energy density of 39 mW h g−1 at a power density of 307 mW g−1 (Fig. S9†). Generally, the power requirements for implantable medical devices fall in the range of micro- to milli-watts.28 These results demonstrate the potential of this rechargeable Zn battery as a viable alternative for powering implantable bioelectronics.
The fact that PEDOT–COOH can be charged and discharged is attributed to the doping/de-doping process in which anions in solution are transferred through the polymer film. To reveal the electrochemical reaction mechanism of the polymer electrodes, the binding energy of S 2p and Zn 2p at various charging/discharging states was analyzed by ex situ X-ray photoelectron spectroscopy (XPS, Fig. 3g). In the S 2p region, the peak intensity of the SO42− anion (2p1/2, 169.5 eV; 2p3/2, 168.3 eV) during the charging process became stronger, proving the insertion of the SO42− anion. Meantime, the high binding energy in PEDOT (2p1/2, 165.5 eV; 2p3/2, 164.3 eV) during the charging process remained constant. The doping level calculated from the peak area ratio of SO42− to PEDOT changed from 11.7% (0.95 V) to 20.0% (1.65 V) and then returned to 12.9% (0.95 V) (Fig. S10†), demonstrating a reversible doping–dedoping process. This doping level was similar to that of conventional polythiophene (0.25 holes per monomer ring) used for rechargeable batteries.29 As for the Zn element, Zn element residuals were observed, probably due to the binding of electrolytes. However, the peak intensity of Zn 2p (1044.9 eV and 1021.9 eV) was almost unchanged during the entire charging/discharging process. The above results rule out the migration of Zn2+ in PEDOT–COOH during the electrochemical processes. To investigate if H+ was involved in the electrochemical reaction, ex situ Raman and XRD characterization techniques were carried out during the charging/discharging process (Fig. S11†). Raman spectra displayed similar curve patterns at different charging stages. The peak intensity of SO42− at 575 and 980 cm−1 continued to increase from 0.95 V to 1.65 V, evidencing the insertion during the charging process. No peak for zinc sulfate hydroxide hydrate (ZHS) can be identified in the Raman and XRD patterns, which may exclude the proton insertion during the charging/discharging process.30,31 In this Zn–polymer battery system, during the charging process, Zn2+ was transferred and reduced on the anode side, while SO42− anions were inserted into the backbone of PEDOT. During discharging, Zn was oxidized and migrated in the electrolyte as Zn2+, whereas the reduction of PEDOT led to the expulsion of the dopants. The main electrochemical reactions were as follows:
At the anode:
Zn + SO42− ↔ ZnSO4 + 2e− |
At the cathode:
2(PEDOT–COOH)+/SO42− + 2e− ↔ 2(PEDOT–COOH)0 + SO42− |
Overall reaction:
Zn + 2(PEDOT–COOH)+/SO42− ↔ 2(PEDOT–COOH)0 + ZnSO4 |
The encapsulated battery was implanted in the dorsal subcutaneous region of SD rats. Since the PVA substrate made up the majority of the battery by mass, it predominantly dictated the degradation process of the device. The external packaging layer was fully resorbed by the SD rat through metabolism after four weeks, along with the leakage of Zn flakes and the PEDOT–COOH film from the edges of the broken implant (Fig. 4b). Traces of the battery components could be observed in the subdermal region after six weeks, followed by their complete disappearance after eight weeks. The in vivo degradation rate was slower than in vitro, attributed to the dynamic environment in the animal body.36 To investigate the effects of biodegradation on the organism, the dorsal tissue close to the implantation sites and major organs were stained with hematoxylin and eosin (H&E) during the biodegradation (Fig. 4c). After four weeks, no obvious macrophage aggregation or inflammatory response was observed, suggesting their biocompatibility. Moreover, the batteries demonstrated negligible toxicity and side effects after eight weeks of complete degradation, as revealed by the H&E staining of main organs such as the heart, liver, spleen, lung, and kidney. The in vitro and in vivo experiments demonstrate the biocompatibility of the battery over the whole life, which was derived from the non-toxic nature of constituent materials and degradation byproducts. Taken together, this polymer-based Zn battery delivered a high output voltage (1.2 V) and high capacity retention at a high rate (51.5%, 10 A g−1). Moreover, it displayed a full biodegradation profile in PBS after 30 days or 56 days in vivo, in contrast to previously reported biodegradable implanted batteries where unreacted active components such as MnO2 and carbon electrodes were left in PBS or in vivo (Table S1†).37–40
Footnote |
† Electronic supplementary information (ESI) available: Experimental electrochemical performance comparison of biodegradable implanted batteries, synthesis, and characterization of monomers and polymers. See DOI: https://doi.org/10.1039/d2sc06342e |
This journal is © The Royal Society of Chemistry 2023 |