Alagarsamy Pandikumar†
*a,
Gregory Thien Soon How†
a,
Teo Peik Seea,
Fatin Saiha Omara,
Subramaniam Jayabal
a,
Khosro Zangeneh Kamalia,
Norazriena Yusoffa,
Asilah Jamilb,
Ramasamy Ramarajc,
Swamidoss Abraham Johnd,
Hong Ngee Lim
be and
Nay Ming Huang
*a
aLow Dimensional Materials Research Centre, Department of Physics, Faculty of Science, University of Malaya, 50603 Kuala Lumpur, Malaysia. E-mail: pandikumarinbox@gmail.com; huangnayming@um.edu.my
bDepartment of Chemistry, Faculty of Science, Universiti Putra Malaysia, 43400 Serdang, Malaysia
cSchool of Chemistry, Centre for Photoelectrochemistry, Madurai Kamaraj University, Madurai-625021, India
dCentre for Nanoscience & Nanotechnology, Department of Chemistry, Gandhigram Rural University, Gandhigram-624302, India
eFunctional Device Laboratory, Institute of Advanced Technology, Universiti Putra Malaysia, 43400, Serdang, Malaysia
First published on 11th November 2014
Dopamine (DA) is an important catecholamine neurotransmitter in the mammalian central nervous system that influences several physiological functions. The impact of DA levels within the human body significantly affects the body functions. Maintaining DA level is essential and the electrochemical detection methods are often used to detect the DA level to regulate the body function. In this review, graphene (functionalized graphene and N-doped graphene) and its composites (metal, metal oxide, polymer, carbonaceous materials, clay, zeolite, and metal–organic framework based graphene composites) modified electrodes with their improved sensing performance towards DA along with several interfering species are described. Further, recent developments on the fabrication of various graphene based composite modified electrodes are also presented. Some important strategies to improve the selectivity and sensitivity towards DA with graphene based composite modified electrodes are also described.
Fig. 3 (A) Cyclic voltammograms and (B) DPV curves obtained for (a) bare GC and chemically modified electrode in the presence of DA, AA and UA. |
The presence of oxygen-containing functional groups in the graphene-based materials play a vital role in the electrochemical sensors, which makes the adsorption and pre-concentration of the redox species (which is of our analytical interest) and effectively catalyse the redox reactions. In addition, the presence of these functional groups makes an effective functionalization with various biomolecules and polymers for applications.65–67 The functionalization of these graphene based materials with specific functional groups can enable the use of these excellent materials for electrochemical sensor applications with specific analytes. The functionalized graphene materials also make fast electron transfer by pre-concentrating the target analytes at the electrode surface. Besides DA, graphene-based materials are also used for electrochemical sensing of other biomolecules such as UA, AA, glucose, cholesterol, folic acid, tryptophan, serotonin and L-dopa.68–72 Among these biomolecules, DA is the most important biomolecule (more details given in Sections 2 and 3) and it is more often used to be detected by graphene (functionalized and N-doped) and their composites with metals, metal oxides, metal–organic frameworks, polymers, clay, zeolite, and carbonaceous materials (Fig. 5).
Fig. 6 Timeline for the development of graphene and their nanocomposite materials based electrochemical detection of dopamine. |
Fig. 7 Different electrochemical pathway for DA and AA on the GO/GCE surface. Reprinted with permission from ref. 73, Copyrights (2013) Elsevier Publications. |
Similarly, Wang et al.73 and Kim et al.84 fabricated an electrochemical sensor using the graphene modified electrode for the sensitive and selective detection of DA. The graphene-modified electrodes displayed better electrochemical performance than MWCNTs modified electrode for selective determination of DA in large excess of AA and was completely eliminating the interference effect of AA. This remarkable increased performance of graphene to DA and AA may be correlated to the elusive 2D structure and unusual electronic properties of graphene. Additionally, the π–π interactions between the aromatic structure of graphene and DA molecules accelerates faster electron transfer rate and at the same time, weakens the AA oxidation at the modified electrode.
Wang and co-workers85 fabricated a facile DA biosensor based on macroporous flower-like graphene-nanosheets cluster (f-RGO) modified glassy carbon electrode (GCE) surface. The obtained modified electrode portraying a large surface area, may provide more active sites for DA oxidation owing to the increased electrolyte-accessible surface area of f-RGO, fast electron transfer process, and the enhancement of DA electrocatalytic performance with good discrimination between DA, AA, and UA in comparison with the bare GCE and layer-stacking RGO/GCE. Yang et al.26 exploited the electrochemically reduced graphene oxide film on GCE (ERGO/GCE) for the simultaneous determination of three electro-active species, namely DA, AA, and UA. The fabricated modified electrode contains unique structural features including high electroactive surface sites and numerous edge plane defects of ERGO favourable for the oxidations of DA, AA, and UA. Hence, this electrode showed reliable recovery for DA in urine samples, indicating that the ERGO is a promising candidate in sensing and biosensing applications. Additionally, Yang et al.86 proposed an ERGO on carbon fiber electrode (CFE) to investigate the electrocatalytic activity towards AA, DA, and UA. The obtained low detection limit for DA (0.77 μM) suggests that the ERGO/CFE showed high sensitivity and selectivity towards simultaneous determination of these biomolecules. Similarly, Zhang et al.87 demonstrates that the partially electrochemical reduced graphene oxide (pERGO) modified electrode showed a significantly high electrocatalytic activity and LOD for the detection of DA which could be attributed to its relatively low background current. In a different study, Raj and John88 reported the fabrication of electrochemically reduced graphene oxide by electrochemical reduction of electrostatically assembled GO on 1,6-hexadiamine (HDA) linker (Fig. 8(A)). The authors claimed that the present modification of ERGO shows advantages as the process does not involve any electrochemical pre-treatment of GCE. Moreover, the amine groups of HDA on the GCE surface does not easily desorbed at a more negative potential. Thus, the ERGO modified electrode displays low surface fouling effect, high stability, and increased electrochemical response towards DA oxidation (Fig. 8(B) and (C)).
Fig. 8 (A) Schematic illustration for the fabrication of ERGO modified GCE, (B) CVs obtained for the oxidation of 0.5 mM of DA at (a) bare GC, (b) GC/HDA/GO, and (c) GC/HDA/ERGO electrodes in 0.2 M PB solution (pH 5.5) at a scan rate of 50 mV s−1. Solid line: first cycle; dotted line: eighth cycle. (C) DPVs obtained for the oxidations of each 0.5 mM of AA, DA, and UA at (a) bare GCE, (b) GC/HDA/GO, and (c) GC/HDA/ERGO electrodes in 0.2 M PB solution. Solid line: first cycle; dotted line: eighth cycle. Reprinted with permission from ref. 79, Copyrights (2013) American Chemical Society. |
Recently, Yu et al.89 reported a three-dimensional (3D) interpenetrating graphene electrode (ErGO) fabricated by the electrochemical reduction of GO for selective detection of DA. The merit of this investigation is that the ErGO electrode was used directly without further functionalization or blending with other functional materials. This electrode can efficiently bring down the oxidation potential of AA to lower potential, thus facilitates to selectively detect DA in the presence of AA and UA. The ErGO modified sensor electrode exhibited a linear response in the concentration range of 0.1–10 μM with a LOD of 0.1 μM DA. Furthermore, this ErGO electrode exhibits good reproducibility and environmental stability, and was used for real sample analysis. Liu et al.90 reported a DA sensor based on graphene-nanosheets paste (GNSP) with the existence of cetyltrimethylammonium bromide (CTAB) for the selective detection DA and AA. In this work, the CTAB acts as a discriminating agent to minimize the fouling effect at the electrode by protecting micelles on the surface of graphene nanosheets. In comparison with graphite paste electrode, GNSP showed enhanced currents for DA and AA which may be related to the promotion of electron transfer by large density of edge/defects sites in the graphene nanosheets and the formation of micelle on the surface of GNS from CTAB aggregation. Hence, the discriminating effect of surfactant in the amplification feature of GNSP greatly improved the sensitivity and selectivity towards DA detection in the presence of interference species.
Nancy et al.91 developed a new strategy for the synthesis of graphene by solar exfoliation method. The resulted solar exfoliated graphene modified electrode (sG/GCE) is utilized for the voltammetric resolution and determination of DA, AA, and UA. Interestingly, the use of binder-free sG/GCE effectively resolved the three electroactive species into well-defined peaks with high potential separations, which was mainly corresponded to the existence of enriched edge planes and oxygenated defects which was demonstrated in the Raman and FTIR analysis in sG sheets. Ying and co-workers92 introduced a novel, disposable, and sensitive screen-printed electrode (SPE) based on ionic liquid doped screen-printing ink which contains graphene (SPGNE) to investigate the electrochemical response of DA, AA, and UA. The screen-printing ink which contains graphite and cellulose acetate, dominates the electrocatalytic performance of SPEs towards different analytes. The developed graphene-based ink electrode coupled with the advantageous properties of graphene and SPE that displayed rich of edge-plane defective sites, shows good antifouling ability, high stability and reproducibility, and rapid electron transfer kinetics which consequently results in the excellent electrochemical performance and well-resolved determination of the co-existing electroactive compounds (DA, AA, and UA).
Recently, Huang et al.93 reported a electrochemical DA sensor with 3D graphene foam (GF). In this study, a three-dimensional macroporous and highly conductive GF was synthesized at atmospheric pressure using chemical vapour deposition (CVD). And then, the sensor electrode was fabricated by transferring the CVD produced GF onto the ITO glass and used for electrochemical detection of DA and AA. The GF electrode exhibits high selectivity for the detection of DA and AA. It also shows high sensitivity for detection of DA with the LOD ∼2.0 nM in the linear response up to ∼10 mM. Furthermore, the 3D GF electrode was used for real samples, drug injection solutions, and human blood serum. Similarly, Yu et al.94 introduced a 3D reduced graphene oxide (3D-rGO) for DA sensor using polystyrene (PSs) as sacrificial templates through a template-assisted self-assembly method. The advantages of the high surface area and the open pore structure of 3D-rGO hinders the aggregation of rGO in aqueous solution, thus leading to a better sensing performance in the selective determination of DA and it showed LOD of 0.17 μM with the linear range of 5 μM–1 mM. The 3D-rGO/GCE showed good stability (97.7% of its initial current response to DA after 10 days storage) and also it shows good reproducibility with RSD of 5.5% and repeatability with the RSD of 4.6%. Hence, it is proven to be an effective functional material candidate in a wide range of applications. Meanwhile, Shang et al.95 demonstrated an efficient and rapid growth of uniform graphene nanoflake films (MGNFs) with sharp edges on Si substrates by substrate-lift-up method using microwave-assisted plasma enhanced chemical vapour deposition (MPCVD) for simultaneous determination of DA, AA, and UA. They established clearly that the novel edge-plane-based electrochemical interface reveals fast electron-transfer (ET) kinetics, active and sensitive electrocatalytic activity which is superior to all bare solid-state (carbon based) electrode, and is only comparable to the edge plane pyrolytic graphite (EPPG) electrode. The significantly enhanced sensing properties of MGNFs are mainly contributed to the special nest-like morphology, large surface area, and edge plane sites/defects acting as the nanoconnectors that can transport the electrons to the underneath substrate.
For the first time, Zhang et al.96 developed a novel and sensitive sensing device for DA based on solution-gated graphene transistors (SGGTs) with functionalized gate electrodes. In this work, the semimetal with zero band-gap of graphene function as both channel and gate electrodes, portraying a stable performance and high sensitivity with a detection limit down to 1 nM in DA determination which is three times much better than that of conventional electrochemical measurements. The authors indicated that the novel sensing mechanism of SGGTs is mainly due to the electrochemical oxidation of DA at the graphene gate electrode which leads to the change of effective gate voltage applied on the transistor (Fig. 9). Besides that, the surface modification on the graphene gate electrode can further improved the sensitivity and selectivity of the sensing device in electroanalysis of different biomolecules.
Fig. 9 (a) Schematic diagram of a SGGT with graphene channel and a graphene gate electrode characterized in electrolyte. (b) Electrochemical reaction of dopamine on the graphene gate electrode. (c) Potential distribution between the gate and the channel of a SGGT in electrolyte. Reprinted with permission from ref. 86, Copyrights (2014) John Wiley and Sons. |
The demonstration of the practical application for the graphene modified electrodes with the quantitative determination in the real samples (human blood serum, urine) by standard addition method is a crucial step in order to study the reliability and applicability of the proposed detection procedure. The recovery results obtained from the spiked samples was found in the range between 97–105% with a small relative standard deviation (R.S.D) in the electrochemical methods. This reflects the effect-free of the interference species (AA, UA, proteins) in the determination of DA and the potential application of graphene modified electrodes for analysing the real samples.
The reported graphene based DA sensors exhibited high sensitivity and excellent selectivity towards the determination of DA. The electrochemical sensing devices introduced by Zhang et al.,96 Huang et al.,93 and Raj and John,88 presents relatively low LODs of DA concentration. Especially in the whole graphene solution-gated graphene transistors (SGGTs) reported by Zhang et al.,96 for the first time it was shown a different working principle from the typical electrochemical instruments. The sensing performance is three times better than conventional electrochemical methods with the detection limit achieving down to 1 nM. The high sensitivity of SGGTs is mainly contributed to the interaction between the analytes and graphene channel, leading to the change of effective gate voltage applied on the transistor in the electro-oxidation of DA at the graphene gate electrodes. Thus, the excellent sensitivity, easy to dispose, and flexible whole-graphene SGGT device can be applied as a potential biosensor in the sensing platform.
Li and co-workers101 prepared an electrochemical DA sensor using N-doped graphene (NG) synthesized by rapid thermal expansion–exfoliation and covalent transformation from melamine (MA)–graphene oxide (GO) mixture (Fig. 10). They studied the relationship of the N-doped configuration (i.e. pyridinic-N, pyrrolic-N and graphitic-N), specific surface area, and electrocatalytic activity towards DA, AA, and UA on the fabricated NGs. Surprisingly, NG modified electrode showed significantly enhanced catalytic activity and excellent electrochemical sensitivity towards simultaneous determination of DA, AA, and UA which is mainly attributed to the large specific area, mesoporous structures, and N doping sites possessed by NG. A larger specific area of NG may provide more N-doping sites for DA oxidation. Furthermore, the formation of strong hydrogen bonds between the pyrrolic-N structure in NG and DA molecules strengthen the interaction between DA and N-doped functional groups and negatively shifts the oxidation peak potentials of DA, AA, and UA. Similarly, Sheng and co-workers80 also introduced N-doped graphene fabricated via thermal annealing of GO and melamine mixture. The synthesized NG used for determining AA, DA, and UA shows enhanced electrocatalytic responses towards oxidation of these species. The increased electrocatalytic activity could be attributed to the unique structure and properties of NG and interaction of hydrogen bond and π–π stack between NG and target biomolecules. Additionally, Li et al.102 successfully developed a modified electrode using N-doped graphene and polyethylenimine (PEI) based on electrostatic layer-by-layer (LBL) self-assembly method. The study demonstrates that the assembled NG multilayer films exhibits fast electron transfer and enhanced current response signals towards oxidation of DA.
Fig. 10 Schematic illustration for the synthesis of N-doped graphene with different allocation of nitrogen-doped configurations at different temperature. Reprinted with permission from ref. 88, Copyrights (2013) Elsevier Publications. |
Among the reported N-doped graphene based DA sensors, the N-doped graphene prepared via thermal annealing of graphene with melamine precursor reported by Sheng and co-workers80 displayed the lowest LOD towards DA sensing.80,101,102 The excellent electrocatalytic performance of NG is mainly attributed to its unique 2D geometric microstructure and properties. The presence of π–π interaction between the aromatic ring of DA molecules and the formation of hydrogen bonds between nitrogen atoms within graphene layers and hydroxyl or amine group in DA molecules, contribute to the enhanced electron transfer kinetics and subsequently decrease the overpotential of biomolecules (AA, DA, UA) oxidation according to their interaction modes. The doping level of pyridine nitrogen in NG samples could tailor the electronic properties in NG and further influenced the electrocatalytic activity of graphene in DA oxidation. Therefore, the NG nanosheets appear as an ideal candidate for a sensitive and selective biosensor.
In the case of functionalized graphene, Wu et al.105 reported a new type of modified electrode using porphyrin-functionalized graphene for the determination of DA. The negatively-charged porphyrin-functionalized graphene electrode stabilizes the chemically reduced graphene and thus facilitates the electron transfer rate at the electrode surface through the π–π stacking interaction and electrostatic attraction whereas the suppression of the oxidation of AA and UA occurs to achieve a low detection limit of 0.01 μM. In another case, Li et al.106 demonstrated a water-soluble sulfonated graphene (sulfonated-G) modified electrode for achieving improved selectivity and sensitivity for DA sensor in the existence of interference species (AA and UA). Similarly, this prepared anion sulfonated-G accelerates electron transfer reaction between the surface of electrode substrate and analytes via the π–π stacking interaction and electrostatic attraction. Moreover, sulfonated-G offers better advancement over conventional Nafion film as the sulfonated-G is water-soluble which maintains the uniqueness and intriguing nature of graphene via electrostatic interactions.
Han and co-workers107 has reported a ferulic acid-functionalized electrochemically reduced graphene oxide (ERGO-FA) employed for the determination of DA in the existence of various interfering species (serotonin, glucose, AA, H2O2, and UA). The prepared ERGO-FA/GCE exhibits good stability, increased selectivity, and sensitivity towards DA via amperometric responses in the DA concentration range of 0.6–1000 μM with the LOD of 0.16 μM (S/N = 3). In a different study, Lian et al.108 utilized an ultrasonic route to synthesize tryptophan-functionalized graphene (Trp-GR) through π–π conjugate action between graphene and tryptophan (Fig. 11). This work reveals that the prepared Trp-GR have well dispersion behaviour in water and better conductivity than pure GR. The resulting Trp-GR/GCE modified electrode achieved excellent electrocatalytic performance for the simultaneous detection of DA, AA, and UA (Fig. 11).
Fig. 11 (a) Schematic diagram of the fabrication procedure Trp-GR, Trp-GR/GCE, and the Trp-GR/GCE was used direct determination of AA, DA, and UA. (b) DPVs of AA, DA, and UA at Trp-GR/GCE in 0.1 M PBS (pH 7.0) respectively, scan rate: 50 mV s−1. (A) AA concentrations: 0.2, 0.4, 0.9, 1.4, 2.4, 3.4, 4.9, 6.9, 8.9, 10.4, and 12.9 mM in the presence of 50 mM DA and 0.5 mM UA; (B) the linear relationship between currents and AA concentration, (C) DA concentrations: 0.5, 1.0, 3.5, 6.0,11, 36, 61, 110, 160, 210, and 310 mM in the presence of 8 mM AA and 100 mM UA; (D) the linear relationship between currents and DA concentration; (E) UA concentrations: 10, 20, 50, 100, 250, 500, 750, 1000, and 2500 mM in the presence of 50 mM DA and 8 mM AA; (F) the linear relationship between currents and UA concentration; (G) DPVs of different concentrations of AA, DA and UA (0.2, 0.45, 0.95, 2, 4, 6, 8 mM) for AA, (2, 7, 12, 50, 75, 200, and 500 mM) for DA and (10, 20, 50, 100, 250, 500, and 750 mM) for UA. Reprinted with permission from ref. 94, Copyrights (2014) Elsevier Publications. |
Zhang et al.109 successfully fabricated a simple, rapid, and selective sensing protocol using a tube-like structure graphene hybrid (GS-PTCA). The preparation of the resulting hybrid involved the combination between graphene sheets (GS) and 3,4,9,10-perylenetetracarboxylic acid (PTCA) via π–π stacking interaction under ultrasonic condition. The proposed hybrid electrode offers improved catalytic activity and selectivity towards the oxidation of DA, AA, UA, and Trp as compared to the pure GS or PCTA. This can be attributed to the synergistic effects between GS and PCTA and also the unique structure of the modified layer PCTA that is enriched with carboxylic functional moieties attached on the surface of GS. In addition, this provides a selective interface to discriminate tracing analytes (DA, AA, UA, and Trp). Wang and co-workers110 developed a modified electrode for the detection of electroactive species (DA, AA, and UA) using 1-butyl-3-methylimidazolium 2-amino-3-mercaptopropionic acid salt ionic liquid functionalized graphene (IL-G/GCE). The superior electrochemical performance in simultaneous DA oxidation responses was mainly attributed to the synergistic effect between graphene and high ionic conductive IL.
Liu et al.111 demonstrated a one pot preparation method for the graphene/ferrocene derivative (graphene/Fc-NH2) nanocomposite by mixing graphene and Fc-NH2 solution. This nanocomposite was used to fabricate the Nafion/graphene/Fc-NH2 modified GCE for the detection of DA. The Fc-NH2 embedded on the graphene significantly enhances the charge-transport ability, stabilizes the graphene, and prevent the leakage of ferrocene. The Nafion/graphene/Fc-NH2/GCE significantly enhanced electrochemical response towards DA due to the synergistic amplification effect between the graphene and Fc-NH2. The peak currents were linearly related to the DA concentrations in the range of 50 nM to 200 μM with the LOD of 20 nM. In the presence of 1 mM AA and 0.1 mM UA, the electrode showed linear response in the range of 0.1 to 4 μM, and the detection limit was 50 nM (S/N = 3). Furthermore, this Nafion/Fc-NH2/graphene/GCE was used for the detection of DA in serum and urine.
Mallesha and co-workers79 studied the electrochemical behaviour of octylamine-intercalated-graphene modified graphite electrode (FCGE) for the selective determination of DA in the presence of UA and AA. In their study, graphene was prepared via the solvothermal reduction of colloidal suspension of graphite oxide in which the FGCE showed excellent electrocatalytic activity towards DA, AA, and UA and successfully resolved the voltammetric signals of AA, DA, and UA into three distinct peaks as compared with that of the bare graphite electrode. Wang et al.112 presented a method in preparing doped graphene into layered double hydroxide films (LDHs) for improving the charge transport of the LDH films for selectively sensing of DA. The high adsorption and catalytic activity of LDHs and superior electrical conductivity of graphene stimulates the strongly enhanced oxidative current response of DA, decreasing the oxidation over-potential as well as resolving the overlapped peak potentials of DA, AA, and UA into three distinct peaks. A summary of the various graphene, N-doped graphene, and functionalized graphene based electrochemical sensors for the detection of DA can be referred in Table 1. Among them, solution-gated graphene transistors (SGGTs) with functionalized gate electrodes showed the lowest LOD for DA (1 nM).
Electrode | Fabrication Method | Detection Method | Linear range (mol L−1) | Limit of Detection | Interference | Real sample | Ref. |
---|---|---|---|---|---|---|---|
a ERGO: Electrochemically reduced graphene oxide; pERGO: partially electrochemically reduced graphene oxide; HDA: 1,6-hexanediamine; MGNFs: microwave plasma produced graphene nanoflake films; PEI: polyethylenimine; CRGO: chemically reduced graphene oxide; TCPP: meso-tetra(4-carboxyphenyl)porphine; Glu: glucose; Trp: tryptophan; PTCA: 3,4,9,10-perylenetetracarboxylic acid; IL-G: 1-butyl-3-methylimidazolium 2-amino-3-mercaptopropionic acid salt; LDH: layered double hydroxide films; CVD: chemical vapour deposition. | |||||||
GO | Covalent coupling | DPV | 1–15 μM | 0.27 μM | AA | — | 83 |
Graphene | Chemical reduction | DPV, CA | 1–200 μM | — | AA | — | 73 |
Graphene | Chemical reduction | DPV | 4–100 μM | 2.64 μM | AA | — | 84 |
Flower-like RGONS clusters | Electrochemical reaction | CV, DPV | 5–7 μM, 0.1–0.6 mM | 3 μM | AA, UA | — | 85 |
ERGO | Electrochemical reaction | CV, DPV | 0.5–60 μM | 50 μM | AA, UA | Urine | 26 |
ERGO/carbon fiber (CF) | Electrodeposition | CV, DPV | 1.5–220 μM | 0.77 μM | AA, UA | — | 86 |
pERGO films | Electrochemical reaction | SWV | 25 nM–5 μM | 20 nM | AA, UA | — | 87 |
ERGO/HDA | Self-assembly | DPV | 5 nM–40 μM | 19 nM | AA, UA | — | 88 |
ErGO | Electrodeposition | CV, AMP | 0.1–10 μM | 0.1 μM | AA, UA | Human serum | 89 |
Graphene nanosheet paste | Chemical reduction | CV, DPV | 4–52 μM | 0.6 μM | AA | Human blood serum | 90 |
Solar graphene | Solar exfoliation | CV, DPV | 20 μM–1 mM | 2.8 μM | AA, UA | — | 91 |
Screen-printed graphene | Chemical reduction | DPV | 500 nM−2 mM | 120 nM | AA, UA | Urine | 92 |
3D-GF | Atmospheric pressure CVD | CV, DPV, AMP | 0.01–10 μM | ∼2.0 nM | AA, UA | Human blood serum sample | 93 |
3D-rGO | Template-assisted self-assembly | DPV, CA | 0.5–1000 μM | 0.17 μM | AA, UA | — | 94 |
Si/MGFs | Microwave plasma enhanced CVD | CV, DPV | 0–100 μM | 170 nM | AA, UA | — | 95 |
Solution-gated graphene transistors | Electrochemical reaction | CA | 1–100 μM | ∼1 nM | Glucose, AA, UA | — | 96 |
N-doped graphene | Thermal expansion–exfoliation | CV, LSV | 100–450 μM | 0.93 μM | AA, UA | — | 101 |
N-doped graphene | Thermal annealing | DPV | 0.5–170 μM | 250 nM | AA, UA | — | 80 |
N-doped graphene/PEI | Hydrothermal | DPV | 1–130 μM | 500 nM | AA | — | 102 |
CRGO/TCPP | Chemical reduction and ultrasonication | DPV | 10 nM–70 μM | 10 nM | AA, UA | Human serum, urine | 105 |
Sulfonated-graphene | Chemical reduction | DPV | 0.2–20 μM | 40 nM | AA, UA | Human serum, urine | 106 |
ERGO-ferulic acid | Chemical reduction, condensation reaction | CA | 0.6 μM–1 mM | 190 nM | Serotonin (5-HT), Glu, AA, H2O2, UA | Human serum | 107 |
Trp-functionalized graphene | Chemical reduction, ultrasonication | DPV | 0.5–110 μM | 290 nM | AA, UA | Human serum, urine | 108 |
Graphene–PTCA | Ultrasonication | DPV | 0.4–374 μM | 130 nM | AA, UA, Trp | — | 109 |
IL/graphene | Chemical reduction | DPV | 5–275 μM | 812 nM | AA, UA | Urine | 110 |
Graphene/Fc-NH2 | Chemical reduction | DPV | 0.05–200 μM | 0.02 μM | AA, UA | Serum, urine | 111 |
Octylamine-intercalated-graphene | Solvothermal reduction | CV, DPV, CA | 0.5–50 μM | 250 nM | AA, UA | Human serum, pharmaceutical samples | 79 |
Graphene-layered double hydroxide films (LDH) | Chemical reduction, doping | CV, SWV | 1–199 μM | 300 nM | AA, UA | Pharmaceutical injections | 112 |
Determination of DA in real samples including urine and blood serum under optimal experimental conditions was performed to evaluate the applicability and feasibility of functionalized graphene modified electrodes in sensing applications. The obtained results are acceptable and satisfactory with the high recoveries of spiked samples ranging from 96.8 to 105% with R.S.D less than 3.0% for the detected samples, indicating that the modified electrode can be utilized for the simultaneous determination of DA in real human serum and pharmaceutical samples.
The highly sensitive and selective DA sensor based on TCPP/CCG constructed by Wu et al.,105 portrayed the best performance in DA oxidation among the reported functionalized graphene electrodes. Owing to the ion exchange membrane and graphene, the π–π stacking and electrostatic interaction between positively charged DA molecules and negatively charged TCPP modified electrode are beneficial to promote the amount of DA molecules on the electrode and accelerate the electron transfer process on the surface of the electrode. Hence, the electrochemical sensor based functionalized graphene emerged as a good potential candidate in biosensing applications.
Many researchers have investigated the usage of metal nanoparticles incorporated graphene nanocomposites modified electrode for the detection of DA. In terms of feasibility, noble metal particles in sub-10 nm dimensions are synthesized which gives this material the merit of higher surface area as compared to various metal oxide nanoparticles. The advantages of the electrochemical oxidation and reduction peaks of noble metals, is they do not overlap with the DA oxidation and reduction peaks that enable these metal nanoparticles to be used for DA sensing.
The gold nanoparticles (Au NPs) incorporated graphene sheets are one of the widely studied materials for biosensor. The significantly lower LOD value feature obtained towards the detection of DA by this graphene–Au NPs composite suggests that this material is suitable in the detection of the trace amount of DA. Li et al.113 reported the fabrication of graphene–Au NPs modified electrode by drop casting the preformed graphene and Au NPs solution on GCE surface. This fabricated graphene–Au NPs/GCE not only significantly improved the electrochemical peak potential separation between DA and AA, but also remarkably enhanced the current response and showed a wide linear concentration range of 5–1000 μM with LOD of 1.86 μM for DA. The graphene–Au NPs/GCE was stored in the refrigerator at 4 °C for two weeks in which the electrode showed the DPV current response of 0.1 mM DA loss of only 5.7% in the initial response, indicating the good stability of the fabricated electrode. Further, the practical application of the electrode was demonstrated by determining DA in blood serum. Yang et al.114 reported a sensitive, rapid, and accurate detection of DA in animal feed at low-cost for clinical diagnostic and therapeutic purposes with disposable ITO substrate embedded rGO–Au NPs. The ITO/rGO–Au NPs modified electrode was fabricated by direct reduction of GO on ITO and then Au NPs were electrochemically deposited by in situ on the ITO/rGO with fairly uniform density and size. The ITO/rGO–Au NPs sensor electrode demonstrates the sensitivity of 62.7 μA mM−1 cm−2 with good selectivity against most common electrochemically interfering species such as AA and UA for DA detection, and the LOD was 60 nM (S/N = 3) by DPV. The ITO/rGO–Au NPs sensor also exhibited good stability and capability to detect DA in beef samples whereby the LOD is consistent with optical sensor.
In another report, Liu and co-workers115 demonstrated a simple, green, and controllable approach for electrochemical synthesis of a ERGO–Au nanocomposite made from ERGO and Au NPs for DA sensor. This nanocomposite possesses the specific features of both Au NPs and ERGO. The electrocatalytic studies concluded that the ERGO–Au NPs/GCE shows better electrocatalytic activity towards DA than bare GCE and its oxidation peak current is linearly proportional to the DA concentration in the range of 0.1–10 μM, with a LOD of 0.04 μM (S/N = 3). Moreover, this ERGO–Au NPs/GCE showed good storage stability, reproducibility, and selectivity. Tian et al.116 reported the synthesis of Au NPsβ-cyclodextrin–graphene-(Au NPs–β-CD–Gra) and modified GCE as a platform for DA sensing. Based on a SWV analysis, three well-resolved oxidation peaks of AA, DA, and UA were obtained for the Au NPs–β-CD–Gra/GCE and it exhibits good linear responses in the ranges 30–2000, 0.5–150 and 0.5–60 μM, respectively. The LODs were found to be 10, 0.15, and 0.21 μM (S/N = 3 and preconcentration time = 3 min) for AA, DA, and UA, respectively.
Chen and co-workers117 demonstrated their DA sensor using highly dispersed hollow gold–graphene nanocomposites (HAu–G) modified electrode. The HAu–G were synthesized by a two-step method, involving the immobilization of hollow gold nanoparticles (HAu NPs) onto the surface of graphene sheets by mixing HAu NPs with a poly(N-vinylpyrrolidone)-functionalized graphene. The HAu–G/GCE electrode exhibits high electrocatalytic activity and extraordinary electronic transport properties. Amperometric detection of DA with this electrode showed a good linearity between 0.08 and 600 μM with a LOD of 0.05 μM (S/N = 3) and also demonstrates good reproducibility and operational stability. The interference of AA and UA was also excluded besides determining the DA in dopamine hydrochloride injection. Yan et al.118 demonstrated the layer-by-layer (LBL) assembled multilayer films of RGO/Au NPs as a sensor electrode for the DA sensor. A polysodium 4-styrenesulfonate (PSS)–RGO and polyamidoamine (PAMAM) dendrimer stabilized Au NPs uses the electrostatic LBL self-assembly on a GCE modified with a poly(diallyldimethylammonium chloride) (PDDA) as a primary layer. The electrochemical studies exhibit the LBL assembled RGO/Au NPs/GCE showing an excellent sensing performance for the detection of DA with LOD of 0.02 μM (S/N = 3) with a linear range from 1 to 60 μM. This sensor electrode further demonstrates the high sensitivity, selectivity, good analytical performance, and long-term stability due to the synergistic effect of RGO and Au NPs with in the LBL assembled films.
The Au NPs were used to decorate on the PEI wrapped graphene nanosheet (GNs) as reported by Ponnusamy et al.119 The mixture of graphene oxide nanosheets (GONS), PEI, and Au(III) undergoes a simultaneous microwave assisted chemical reduction to form GNS/PEI/Au NPs composite. The sodium borohydride (NaBH4) was employed to further reduce the unreduced site of GONS and HAuCl4 in the PEI solution. This modified electrode gives a detection limit of 200 nM with a sensitivity of 0.2 μA μM−1 cm−2. It is anticipated that an extensive research regarding the modification and development of new graphene–polymer based composite will be done in the future for improving the sensitivity of DA sensor. Liu et al.120 reported a novel platform constructed for DA sensor based on RGO and Au NPS entrapped into the chitosan/silica sol–gel hybrid membranes (RGO–AuNPs–CSHMs). The hybrid membranes are prepared by cross-linking CS with APTES, while the presence of RGO and Au NPs that improves the conductivity of CSHMs. The RGO–AuNPs–CSHMs modified electrode exhibit enhanced sensitivity towards the oxidation of DA and UA and the CV and DPV techniques showed well defined and separated oxidation peaks for DA and UA with linear range of 1–200 μM and 1–300 μM, respectively. The LOD was found to be 0.3 and 0.7 μM for DA and UA, respectively.
Qian et al.121 fabricated the Au NPs decorated PPy/RGO hybrid sheets for electrochemical DA sensor. The Au NPs–PPy/RGO hybrid sheets prepared via an in situ chemical oxidative polymerization process, which showed crumpled and wrinkled surface of this composite along with the uniform flower-like Au nanoparticles and thus significantly improved the electrochemical properties of the modified electrode with surprisingly, an extremely low LOD of 18.92 pM and a remarkable sensitivity of 16.40 μA μM−1 with a linear range of 0.1–5000 nM. Qian and co-workers used Au NPs coated polystyrene/reduced graphite oxide (PS/RGO) core shell microspheres via a facile process.122 They have mixed PS/RGO core shell microspheres and AuCl4 in aqueous solution by ultrasonication method before reducing the mixture together using trisodium citrate, NaBH4, and hydrazine hydrate via heat treatment. The Au NPs–PS/RGO microsphere modified electrode has shown an improvement in the sensibility of electrochemical detection for DA as low as 5 nM with a sensitivity of 3.44 μA μM−1 due to the unique chemical and electrical properties of citrate reduced Au NPs. Moreover, the coating of Au NPs also prevented the aggregation of RGO which then enhances the dispersibility and electrical conductivity of the composite.
Kaur et al.123 reported a simple synthetic method for the preparation of Ag NPs decorated rGO composite (Ag NPs/rGO), by heating the mixture of GO and AgNO3 in the presence of NaOH. The Ag NPs/rGO was used to fabricate the sensor electrode for the simultaneous detection of UA, DA, AA, and Trp. The Ag NPs/rGO modified electrode exhibited excellent electrocatalytic activity, stability, sensitivity, and selectivity with well-separated oxidation peaks toward UA, DA, AA, and Trp. The higher electrocatalytic activity of Ag NPs/rGO is attributable to the facile transportation of electrons and reactant/product molecules due to the high surface area of GO and the uniform favorable distribution of Ag nanoparticles on rGO, providing a considerable surface enhancement effect to AA, DA, UA, and Trp, which significantly increases their oxidation current signals. The analytical performance of this Ag NPs/rGO composite material was demonstrated for the determination of AA and DA in commercial pharmaceutical samples such as vitamin C tablets and DA injections, respectively. Recently, Cincotto et al.124 demonstrated the preparation of ∼20 nm sized Ag NPs decorated mesoporous silica/graphene oxide (SiO2/GO) hybrid material by using DMF as a reducing agent. The Ag NPs/SiO2/GO hybrid material was used to develop a sensitive electrochemical sensor for the simultaneous determination of epinephrine (Ep) and DA. The study demonstrates that the resultant Ag NPs/SiO2/GO-modified electrode is highly sensitive for the simultaneous determination of DA and Ep with the LOD of 0.26 and 0.27 μM, respectively. The improved selectivity and sensitivity of this modified electrode is due to the synergistic effect characteristic of Ag NPs, SiO2, and GO in the hybrid material. The Ag NPs/SiO2/GO-modified electrode is highly selective and was used to detect the DA and Ep in human urine samples.
Xu et al.125 demonstrated a simultaneous electrochemical detection of DA, UA, and AA using Pt/reduced graphene oxide (Pt/RGO) modified GCE. The Pt/RGO nanocomposite was prepared by the chemical reduction of H2PtCl6 and GO, and was used for electrode modification. The Pt/RGO/GCE modified electrode showed good performance towards the individual and also simultaneous detection of DA and UA in the presence of 1 mM AA. The oxidation peak currents showed linear relationship with the associated DA and UA concentrations in the range of 10–170 μM and 10–130 μM, respectively, with the LOD of 0.25 μM for DA and 0.45 μM for UA (S/N = 3). The electrode showed good reproducibility and the RSDs of the peak currents of 30 successive runs are 3.75 and 3.22% for DA and UA, respectively, which are both lower than 4%, and it suggest that the Pt/RGO/GCE is not subjected to surface fouling effect by the oxidized products. Zhi-Quan and co-workers126 reported the graphene–poly(styrene sulfonate)–Pt nanocomposite (GN–PSS–Pt) based DA sensor. A clean and facile microwave-heating procedure was used for the preparation of well-dispersed GN–PSS–Pt nanocomposite by using microwave-heating method. The GO and chloroplatinic acid could be simultaneously reduced with ethylene glycol and used for electrochemical study. In this study, a chronoamperometric technique was used for the DA detection and the electrode showed the linear range of 200 nM to 4 mM with the LOD of 40 nM (S/N = 3). The GN–PSS–Pt/GCE showed good repeatability, even when the electrode was subjected to the oxidation of 300 μM of DA for 11 times which stills exhibit a satisfying repeatability with a RSD of 4.3%. The response of the electrode for 300 μM DA was 92.5% of its initial current response after storage for 10 days. The modified electrodes exhibit good selectivity toward DA sensing in the presence of interfering species Ca2+, K+, Na+, Zn2+, Cl−, Mg2+, CH3COO−, SO42−, H2PO4−, HPO42−, UA, and AA. Moreover, the GN–PSS–Pt modified electrode was applied for the determination of DA in human urine and serum samples.
Li et al.74 reported a one pot preparation method to prepare a water-soluble and electroactive composite, Pt NPs/polyelectrolyte-functionalized ionic liquid/graphene sheets (Pt/PFIL/GS) by chemical reduction. The obtained Pt/PFIL/GS nanocomposite was used to fabricate the modified electrode for the simultaneous detection of AA and DA. The difference between the oxidation potentials of AA and DA is over 200 mV, which leads to the ability to distinguish AA from DA. The obtained potential difference is due to π–π interactions between the phenyl structure of DA and planar hexagonal carbon structure of graphene which facilitates the easy arrival of DA molecules to the surface of modified electrode. Although the π–π interaction between penta-heterocycle of AA and planar hexagonal carbon structure of graphene is weak, the presence of cationic PFIL provides a remarkable electrostatic attraction to the negatively charged AA and rejection to positively charged DA in PBS (pH 7.0) due to the charged characteristic of AA (pKa = 4.10) and DA (pKa = 8.87). The electrostatic force leads to the realization of AA oxidation at the Pt/PFIL/GS-modified electrode. The sensor electrode was further used for real sample analysis (human urine), and it showed independent oxidation peaks for urine sample containing AA and DA. In another report,127 size-selected Pt nanoparticles with a mean diameter of 1.7 nm were self-assembled onto the graphene surface and was used for the simultaneous electrochemical detection of AA, DA, and UA. Based on the DPV technique, DA in the presence of UA and AA depicts three isolated peak separation potentials were 185 mV (AA to DA), 144 mV (DA to UA), and 329 mV (AA and UA), respectively, indicating the good selectivity of the Pt/graphene modified electrode.
Chen and co-workers128 studied the electrochemical sensing behaviour of palladium-electrochemically reduced graphene oxide (Pd NPs/RGO) modified electrode towards DA. The Pd NPs/RGO modified electrode showed a DA oxidation peak at 0.25 V. Upon increasing the concentration of DA, the oxidation peak current increased linearly, but the reduction peak current decreased which is due to the high surface area and high conductivity of Pd NPs/RGO nanocomposite. Further, it showed a linear concentration range of 1–150 μM and LOD of 0.233 μM (S/N = 3) with a sensitivity of 2.62 μA μM−1 cm2. Instead of using ERGO, another study reported a chemically reduced graphene oxide (CRGO) sheets which was used in the nanocomposite for the DA sensor.129 The presence of CRGO in the Pd NPs/CRGO/GCE electrode enhances the surface coverage concentration and also increases the electron transfer rate constant. The Pd NPs/CRGO/GCE showed two well separated oxidation peaks for the detection of DA and diclofenac in a mixture with a linear range of 2–63 μM and was further used for the simultaneous detection of DA and diclofenac in real samples with a linear range of 2–50 μM. Wu et al.130 reported a high-performance non-enzymatic electrochemical sensor using high-conductivity and large-surface-area graphene supported Pd NPs in the presence of supercritical CO2 fluid (scCO2). The merit of using the scCO2 is that they can de-bundle the graphene nanosheets and uniformly disperse the Pd NPs (∼3 nm), thereby effectively suppressing the restacking of graphene. The Pd NPs are sandwiched between the highly conductive sheets leading to superior electrochemical utilization. Consequently, the Pd/graphene@scCO2 exhibited significantly higher sensitivity and selectivity for AA, DA, and UA as compared to those of the plain graphene and Pd/graphene@air electrodes. The electrode showed sensitivity of 287 μA μM−1 cm2 and LOD of 0.1 μM (S/N = 3) for DA with co-existence of 1 mM AA and 50 μM UA.
Jiang and co-workers131 described the one-step in situ reduction process for the preparation of bimetallic Pd–Pt nanoparticles anchored on functionalized reduced graphene oxide (RGO) nanocomposite, in which Pt and Pd ions were firstly attached to PDDA-functionalized graphene oxide (GO) sheets and then the encased metal ions and GO were subjected to simultaneous reduction by ethylene glycol. An electrochemical sensor based on the Pd3Pt1/PDDA–RGO nanocomposites was fabricated for the simultaneous detection of AA, DA, and UA in their ternary mixture and it showed three well-separated voltammetric peaks along with remarkable increasing electro-oxidation currents by DPV technique. Under the optimized conditions, the linear relationships between the peak currents and the concentrations were in the range of 40–1200 μM (AA), 4–200 μM (DA), and 4–400 μM (UA) with LOD (S/N = 3) of 0.61, 0.04, and 0.10 μM for AA, DA, and UA, respectively. The improved sensing performance can be attributed to the synergistic effect of Pd–Pt bimetallic nanoparticles and RGO. Further, the practical utility of the sensor electrode was demonstrated by the determination of AA, DA, and UA in human urine and blood serum samples.
Recently, Jiang and co-workers132 have reported reduced graphene oxide-supported Au@Pd (Au@Pd–;RGO) nanocomposites for the simultaneous determination of AA, DA, and UA (Fig. 12). The fabricated Au@Pd–;RGO electrodes show good sensing properties due to their large surface area and the conductivity of RGO. Hence, the linear response ranges were 1–800 μM, 0.1–100 μM, and 0.1–350 μM with the LOD of 0.28, 0.024, and 0.02 μM for AA, DA, and UA, respectively. A summary of the various graphene–metal nanocomposites based electrochemical sensor in the detection of DA can be referred in Table 2.
Fig. 12 Schematic Illustration of preparations of (A) Au@Pd–RGO nanocomposites and (B) Au@Pd–RGO/GCE sensors for simultaneous determination of AA, DA, and UA. (C and E) From bottom to up 60 the concentrations of AA from 1 to 800 μM, DA from 0.1 to 100 μM, and UA from 0.1 to 350 μM. (D and F) Plots of the oxidation peak currents against the concentrations of AA, DA, and UA, respectively. The error bars represent standard deviations for five tests. Reprinted with permission from ref. 120, Copyrights (2014) Royal Society of Chemistry. |
Electrode | Fabrication method | Detection method | Linear range | Limit of detection | Interference | Real sample | Ref. |
---|---|---|---|---|---|---|---|
a Au: gold nanoparticles; β-CD: β-cyclodextrin; ERGO: electrochemically reduced graphene oxide; RGO: reduced graphene oxide; PSS: polysodium 4-styrenesulfonate; PEI: polyethylenimine; CSHMs: chitosan/silica sol–gel hybrid membranes; Ag: silver nanoparticles; Pt: platinum nanoparticles; PFIL: polyelectrolyte-functionalized ionic liquid; Pd: palladium nanoparticles; PDDA: poly(diallyldimethylammonium chloride). | |||||||
Au–graphene | Chemical reduction | DPV | 5–1000 μM | 1.86 μM | DA, AA | Human serum | 113 |
Au/RGO | Reflux | ECL | 0.02–40 μM | 60 nM | DA, UA, AA | — | 114 |
ERGO–Au NPs | Electrochemical reduction and deposition | 0.1–10 μM | 0.04 μM | NaCl, KNO3, MgSO4, UA, AA, Glu, Cys, CA, TA, Lys | Dopamine hydrochloride injection, urine | 115 | |
Au–β-CD–graphene | Chemical reduction | SWV | 0.5–150 μM | 150 nM | DA, UA, AA | Urine | 116 |
HAu–graphene | Chemical reduction | DPV | 0.08–600 μM | 50 nM | DA, UA, AA | — | 117 |
Au@PSS–graphene | Chemical reduction | DPV | 1–60 μM | 20 nM | DA, UA, AA | — | 118 |
G/PEI/Au | Chemical reduction | DVP | 2–48 μM | 200 nM | DA, AA | Urine | 119 |
RGO–AuNPs–CSHMs | Chemical reduction | DPV | 0–200 μM | 50 nM | DA, UA, AA, Glu | Urine | 120 |
Au@PPy/RGO | Chemical reduction | DPV | 0–5 μM | 18.92 pM | DA, UA, AA | Urine, human serum | 121 |
Au–PS/RGO | Chemical reduction | DPV | 0.05–20 μM | 5 nM | DA, UA, AA | Human serum | 122 |
Ag/RGO | Reduction | LSV | 10–800 μM | 5.4 μM | DA, UA, AA, Trp, Na+, K+, Mg2+, Zn2+, Glu | Urine | 123 |
Ag NPs/SiO2/GO | In situ chemical reduction | 2–80 μM | 0.26 μM | UA, AA, EA | Urine | 124 | |
Pt/RGO | Chemical reduction | DPV | 10–170 μM | 250 nM | DA, UA, AA | — | 125 |
GN–PSS–Pt | Microwave reduction | CA | 20 nM–4 mM | 40 nM | Ca2+, K+, Na+, Zn2+, Cl−, Mg2+, CH3COO−, SO42−, H2PO4−, HPO42−, UA, AA | Urine, human serum | 126 |
Pt/PFIL/GS | Chemical reduction | DPV | — | — | DA, UA, AA | Urine | 74 |
Graphene/Pt | Reflux | DPV | 0.03–8.13 μM | 30 nM | DA, UA, AA | — | 127 |
RGO–Pd | Electrochemical reduction | LSV | 1–150 μM | 233 nM | DA, UA, AA, Glu | — | 128 |
Pd–RGO | Electrochemical reduction | LSV | 2–63 μM | — | DA, UA, AA, Glu | Urine | 129 |
Pd–RGO | Chemical reduction | DPV | 2–10 μM | 100 nM | DA, UA, AA | — | 130 |
Pd3Pt1/PDDA–RGO | Chemical reduction | DPV | 4–400 μM | 110 nM | DA, UA, AA | Urine, human serum | 131 |
Au@Pd–RGO | Reduction | DPV | 0.01–100 μM | 2 nM | DA, UA, AA, Cl−, NO3−, CO32−, SO42− | Urine | 132 |
In real sample analysis involving blood serum and urine, few reported works involving the use of GN–PSS–Pt, graphene/Pd–Pt, Au/graphene, AuNPs/PS/RGO microspheres, and Au/PPy/RGO to detect DA with high amount of recovery.113,121,122,126 Similarly, other graphene–metal nanocomposites also showed applicability in the detection of DA in real conditions. Among the reported graphene–metal nanocomposites, the Au@PPy/RGO modified electrode reported by T. Qian et al.108 is the most promising choice because they have achieved the lowest LOD. This nanocomposite features offer the formation of flower-like Au nanoparticles into the PPy/RGO which exhibits a unique structure, thus enhancing the electrical conductivity that leads to the excellent electrocatalytic activity towards DA.
Fig. 13 (a) Mechanism for the electrocatalytic oxidation of dopamine at rGO/TiO2 {001} modified GCE. (b) DPV obtained for rGO/TiO2 {001} modified GCEs during the addition of 1, 2, 4, 8, 10, 15, 25, 30, 35, 40, 50, 60, 80, and 100 μM DA into the 0.1 M PBS (pH = 6.5). (c) Calibration plot observed for the oxidation peak current vs. concentration of DA. Reprinted with permission from ref. 123, Copyrights (2014) Nature publishing Group. |
Another graphene–metal oxide nanocomposite that utilizes the electrical conductive and superparamagnetism properties of Fe3O4 on reduced graphene oxide sheets (Fe3O4/r-GO) was reported by Teymourian et al.135 A simple chemical reduction method using hydrazine hydrate to form Fe3O4/r-GO proves superior in the enhancement of bioelectrochemical sensing of various analytes such as NADH, lactate, O2, and H2O2. In the context of DA, their modified GCE shows clear separation of peak potentials of DA, AA, and UA with LOD of 0.08, 20.0, and 0.50 μM, respectively. However, the use of hydrazine and hydrazine hydrate compounds are not favourable in terms of their high toxicity and instability. Another nanocomposite based on Fe3O4 was also reported using amino-group functionalized mesoporous Fe3O4 on graphene sheets (Fe3O4–NH2@GS).136 Their Fe3O4–NH2@GS/GCE shows high sensitivity and selectivity towards simultaneous detection of DA, AA, and UA. Hence, this nanocomposite offers high biocompatibility and good electrocatalytic oxidation which is simple and environmental friendly to produce. Salamon et al.137 reported the magnetite nanorods anchored over rGO synthesized through a simple and time efficient one pot method (rGO/Fe3O4). Interestingly, the LOD for the rGO/Fe3O4 composite achieved a value of 7 nM towards the detection of DA owing to the large surface area of GO which provides high electrical conductivity, biocompatibility, and aromatic sp2 bonds for the facile transportation of electrons. In addition, the cubic spinel structure of the Fe3O4 nanorods also increases adsorption therefore enhancing electrocatalytic activity. We have also reported an iron oxide/graphene modified glassy carbon electrode (Fe3O4/rGO/GCE) and its simultaneous detection of DA and AA, in which the Fe3O4/rGO was prepared through a one step in situ wet chemical method.138 Through this, the detection limit of Fe3O4/rGO/GCE was found to be 0.42 and 0.12 μM for AA and DA in the concentration range of 1–9 mM and 0.5–100 μM showing the possible use of Fe3O4/rGO as a potential electrode material.
Tin dioxide on graphene sheets used in modifying carbon ionic liquid electrode (GR–SnO2/CILE) was first introduced by Sun et al.139 for electrochemical sensing application. They reported the detection of DA with a detection limit of 0.13 μM even under high dosage of UA as the interference compound. Moreover, the modified electrode exhibits excellent recovery of DA in the injection samples. Similarly, another report was described on graphene oxide (GO) functionalized with sodium dodecyl sulphate to synthesize graphene nanosheet/SnO2 nanoparticle hybrid nanocomposite (SDS–GN/SnO2).140 The use of SDS in the nanocomposite prevents the restacking of graphene layers and enhanced the electrochemical properties in which the SDS–GN/SnO2/GCE portray a LOD of 80 nM in determining DA and also high recovery of DA in human urine tests. However, the use of hydrazine hydrate in their synthesis method still remains a negative impact.
Other graphene–metal oxide nanocomposite studies includes the use of cuprous oxide decorated on graphene sheets (Cu2O/graphene) reported by Zhang et al.141 Their nanocomposite offers uniform Cu2O nanoparticles broadly distributed on graphene sheets through a solvothermal route in ethylene glycol. Based on their CV studies, their Cu2O/graphene/GCE denotes a good LOD of 10 nM in detecting DA but increases to 200 nM as UA was added as the interference effect with the selectivity properties still satisfactory. As mentioned above, most of the studies employ graphene as their platform to grow metal oxides nanostructures. Nonetheless, an investigation was reported in using SiO2 coated GO instead as a surface to prepare molecularly imprinted polymers (GO/SiO2–MIPs) composites.142 This interesting method prepares GO/SiO2 through sol–gel process and the introduction of vinyl groups onto GO/SiO2 with γ-methacryloxypropyltrimethoxysilane (γ-MAPS) and finally copolymerization. Indeed, their fabricated GO/SiO2–MIPS/GCE shows promising electrochemical sensing properties and excellent selective characteristics of DA over AA, UA, norepinephrine (NE), and epinephrine (EP). Ma et al.143 reported a three-dimensional graphene (3DGN)@WO3 nanowire sensor in detecting H2O2, AA, and DA. Their unique structure shows promising results in high electrocatalytic activities which have the potential to act as a scaffold support and as a real time sensor monitoring analytes. Lastly, Nayak et al.144 reported a Nafion coated ZnO nanoparticles decorated graphene sheets (ZnO–sG–Nafion) as a transducer candidate. Their fabricated modified electrode shows a good linear amperometric response from 10 M to 800 M with a LOD of 1 M. A summary of the various graphene–metal oxide nanocomposites based electrochemical sensor in the detection of DA can be referred in Table 3.
Electrode | Fabrication method | Detection method | Linear range | Limit of detection | Interference | Real sample | References |
---|---|---|---|---|---|---|---|
a 4-ABAS: 4-aminobenzenesulfonic acid; SDS: sodium dodecyl sulfonate; MIPS: molecularly imprinted polymers. | |||||||
TiO2–graphene | Hydrothermal | DPV | 5–200 μM | 2 μM | AA, UA | — | 75 |
TiO2–GR/4-ABAS | Hydrothermal & electropolymerization | DPV | 0.4–10 μM | 0.1 μM | Trp | Human serum | 133 |
rGO/TiO2 {001} | Solvothermal | DPV | 2–60 μM | 1.5 μM | AA | — | 134 |
Fe3O4/r-GO | Chemical reduction | DPV | 0.4–3.5 μM | 0.08 μM | AA, UA | — | 135 |
Fe3O4–NH2@GS | Solvothermal | DPV | 0.2–38 μM | 0.126 μM | AA, UA | Urine | 136 |
rGO/Fe3O4 | Reflux | CA | 0.01 to 100.55 μM | 7 nM | AA, UA, CA, HA, AP, NaCl, Glu | Urine | 137 |
Fe3O4/rGO | Chemical reduction | DPV | 0.5–100 μM | 0.12 μM | AA | — | 138 |
GR–SnO2 | Ultrasonication | DPV | 0.5–500 μM | 0.13 μM | UA | — | 139 |
SDS–GN/SnO | Chemical reduction | DPV | 0.1–10 μM | 80 nM | AA, UA | Urine | 140 |
Cu2O/graphene | Solvothermal | CV | 0.1–10 μM | 10 nM | UA | — | 141 |
GO/SiO2–MIPS | Sol–gel | CA | 50 nM–0.16 mM | 30 nM | NE, EP, AA, UA | Urine | 142 |
3D-GN@WO3 nanowire | CVD & hydrothermal growth | CA | 10–150 μM | 238 nM | CS, UA, AA, Glu, Frc, CC, NaCl | — | 143 |
ZnO–sG–Nafion | Mechanical mixture | CA | 10–800 μM | 1 μM | AA, UA | — | 144 |
The real sample analysis was carried out in few reported works involving human serum and urine and the recovery of DA achieved 90 to 110%, indicating the potential use of graphene–metal oxide nanocomposite to modify electrochemical sensor for practical application. Among the reported metal oxides incorporated graphene nanocomposites, the rGO/Fe3O4 modified electrode have the lowest LOD of 7 nM for DA detection which also indicates good reproducibility (RSD = 2.85%) and remarkable anti-interference effect when AA and UA was added into the DA based solution.137 This fabrication method is quite promising in applying the graphene–metal oxide nanocomposite unique features as it involves a one-pot preparation route without the addition of surfactants making it an ideal choice. Based on all of this, there is still room for more investigation on graphene–metal oxide based nanocomposites for electrochemical sensing of DA as this field is still not widely explored. Hopefully, future works would hold promising results in the key of producing cheaper and greener composite materials for electrochemical sensing applications.
Various synthetic routes have recently been reported for the fabrication of graphene–polymer based composite including together-blending via ultrasonication,105,155 heat treatment,156 microwave assisted chemical reduction,119 and electropolymerization techniques.147,157 Electropolymerization method has been paid the most attention because it permits the regulation of the spatial location and selective control of the material properties through variation of the polymer monomer, the potential window, and the electrolytic conditions during the electrodeposition process.158 In addition, this method also provides a simple, fast, and direct procedure. A report by Liu et al. described the electropolymerization process to fabricate PVP/graphene on top of GCE surface.147 A drop of GO solution was dropped on the clean GCE surface before CV scans was carried out for five times. Then, the process continued by drop casting the PVP solution on top of the graphene/GCE surface to form PVP/graphene/GC modified electrode. Likewise, Liu and co-workers157 developed a poly(o-phenylenediamine) (PoPD)/graphene hybrid composite using electropolymerization technique where electropolymerization of o-phenylenediamine was performed on the graphene/GC electrode. This modified electrode was then used as a working electrode in the electrochemical cell for the detection of DA in human urine samples. The carbon paste electrode (CPE) was also frequently used in sensor application. A novel technique to prepare a graphene/chitosan nanocomposite modified on the surface of CPE has been reported by Chang et al.155 The reduction process of graphite was done by adding graphite flakes in a mixture of N,N-dimethylformamide and acetic acid via ultrasonication. Next, the chitosan was added in the mixture to form graphene/chitosan composite, before being used to modify the CPE. Han et al. had synthesized graphene/chitosan composite by a together-blending and in situ chemical reduction method.76 This composite was then being used to modify GC electrode for determination of DA. The result shows that the modified CPE exhibited an improved DA sensing compared to the modified GC electrode. Based on these studies, due to the expensive manufacturing cost of GCE and better sensing performance of modified CPE, graphene/polymer composite modified CPE has emerged as one of the potential working electrode to replace graphene/polymer composite modified GCE in the future for DA sensor application.
Yan and co-workers159 reported a novel high-performance organic electrochemical transistors (OECT) based DA sensor with functionalized gate electrodes. The selectivity of the fabricated biocompatible polymers (Nafion or chitosan) modified gate electrodes was significantly improved with the help of Nafion or chitosan which can be attributed to the different electrostatic interactions between the polymer films and the analytes. Meanwhile, the sensitivity of the devices was improved by using graphene nanomaterials including graphene and rGO because of the excellent charge transport properties and high surface to volume ratio of graphene flakes. The devices modified with Nafion–graphene showed the detection limit down to 5 nM with broader linear range from 5 nM to 1 μM and excellent selectivity towards DA. A summary of the various graphene–polymer composites based electrochemical sensor in the detection of DA can be referred in Table 4.
Electrode | Fabrication method | Detection method | Linear range | Limit of detection | Interference | Real sample | References |
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a PVP: polyvinylpyrrolidone; PANI: polyaniline; PPy: polypyrrole; PEDOT: poly(3,4-ethylenedioxythiophene); PpPD: poly(p-phenylenediamine); PoPD: poly(o-phenylenediamine); GSCR-MIPs: Congo red-molecular imprinted polymers; EDTA–silane: N-(trimethoxysilylpropyl) ethylenediamine triacetic acid. | |||||||
Graphene/PVP | Electrochemical reduction and electropolymerization | CA | 500 pM–1.13 mM | 200 pM | AA | Urine, human serum | 147 |
RGO/PEDOT | Electrodeposition and electrochemical reduction | CA | 0.1–175 μM | 39 nM | AA, UA | — | 148 |
Graphene/polystyrene | γ-ray irradiation-induced graft polymerization, solvothermal | DPV | 5–100 μM | — | — | — | 149 |
Graphene/PANI | In situ polymerization, electrochemical apta sensor | SWV | 7 pM–90 nM | 1.98 pM | AA, tyramine, l-3-hydroxytyrosine | Human serum | 150 |
RGO/PPy | In situ chemical oxidative polymerization | DPV | 1 nM–8 μM | 0.3 nM | AA, UA | Human blood serum | 151 |
Graphene/porphyrin | Condensation and electrochemical reduction | DPV | 0.1–500 μM | 35 nM | AA, 5-HT | — | 152 |
Graphene/chitosan | Layer-by-layer assembly | DPV | 0.1–140 μM | 50 nM | UA | — | 153 |
EDTA–silane/RGO/Nafion | Silanization and ultrasonication | DPV | 0.2–25 μM | 10 nM | AA | — | 154 |
Graphene oxide/PANI | In situ chemical polymerization | DPV | 2–18 μM | 500 nM | AA, UA | — | 155 |
Graphene/chitosan | Chemical reduction and ultrasonication | DPV | 0.2–100 μM | 98.2 nM | AA, UA | — | 76 |
RGO/PpPD | Heat treatment | CA | 5–25 μM | 360 nM | AA, UA | — | 156 |
Graphene/PoPD | Electrochemical reduction and electropolymerization | DPV | 10–400 mM | 7.5 mM | AA, UA | Urine | 157 |
Graphene sheets/GSCR–MIPs | Free radical polymerization | CA | 0.1–830 μM | 100 nM | — | — | 158 |
Graphene/chitosan | Blending and chemical reduction | DPV | 1–24 μM | 1 μM | AA, UA | — | 159 |
T. Qian and co-workers139 had used RGO–HDPPy modified GC electrode for DA analysis in human blood serum and the result revealed 99.4 to 102.4% recovery. Meanwhile, a novel electrochemical aptasensor of GR-PANI modified GC electrode fabricated by S. Liu et al.138 shows good recovery values from 99 to 105% after tested in human blood serum. Other than that, the PVP/GR/GCE was also applied in the determination of DA (urine samples) that displays 97.9 to 101.4% recovery.135 The applicability of these electrode for determination of DA in real samples were fairly good, hence it possesses an excellent potential in sensor application.
Obviously, among the reported works, the GR/PANI modified electrode reveals a significantly low LOD of 1.98 pM for DA detection and have shown an excellent potential for the practical application in DA analysis with 99 to 105% recovery after tested in human blood serum sample. This excellent result was due to the presence of an aptamer in this novel label-free electrochemical aptasensor that is so well attached onto the GR–PANI surface which is used in capturing DA molecules. The interaction between the aptamer and DA molecules will induce a current response which is transferred through an excellent electron transfer activity provided by the GR-PANI nanocomposite. Therefore, this action will increase the sensitivity and selectivity of the sensor which is able to provide a very low LOD in the pM range.
Nickel foam is a fascinating material that can be used as a growth substrate due to its high biocompatibility. As reported by Dong et al.,161 the electrochemical DA sensor was fabricated based on a 3D graphene–CNT hybrid foam synthesized using two-step chemical vapour deposition (CVD) approach under atmospheric pressure. Serving as a free-standing electrode, their 3D hybrid electrode results in an excellent amperometric signals for detection of DA with a low detection limit of 20 nM (S/N = 9.2) and high sensitivity of 470.7 mA M−1 cm−2. In addition, the material was also applied for the determination of H2O2, which can be indirectly detected with the assistance of enzymes. Interestingly, they have modified the 3D hybrid electrode with horseradish peroxidase (HRP) and Nafion which results in an amperometric response of high sensitivity (137.9 mA M−1 cm−2), low detection limit of 1 μM (S/N = 17.4), and a wide linear detection range (10 μM–1 mM). In the case of electrochemical detection of DA with the co-existence AA and UA, Sun et al.162 developed core–shell MWCNT–graphene oxide nanoribbons (GONRs)-modified GCE for the simultaneous detection of the DA, AA, and UA. The GONRs was fabricated by the microwave-assisted facile unzipping of MWCNTs producing powder form. To prepare the modified electrode, the powder was mixed with deionized water, ethanol, and Nafion. The well-resolved corresponding peak potential separations of 229.9 mV (AA to DA), 126.7 mV (DA to UA), and 356.6 mV (AA to UA) were achieved. In addition, the amperometric response displayed a low LOD for AA, DA, and UA as 60, 80, and 70 nM, respectively.
In another study involving quantum dots, it has been used in many bio-analytical applications due to their large surface area and good stability. Hu et al.163 fabricated reduced graphene oxide (rGO)/carbon dot (CD) composite film for highly selective and sensitive detection of DA with the interference of AA and UA. CDs are novel due to their zero-dimensional carbon materials which could effectively prevent the aggregation of graphene. The composite was prepared by adding GO solution to CD solution and placed into an autoclave for 4 h at 90 °C. In this process, CDs acts as the reducing agent which can reduce GO to rGO and were applied to GCE using a micro injector. By using DPV analysis technique, the composite responded linearly to DA in a wide concentration range from 0.01 to 450.0 μM with a low detection limit of 1.5 nM. In addition, the composite also showed high stability which could keep its activity for at least two weeks. Interestingly, the addition AA and UA still did not interfere in the DA determination capability. This is due to the cationic exchanger of rGO/CDs/GCE that selectively attracts cationic DA and prevents anionic AA and UA from reaching the GCE surface. Likewise, Chen et al.164 reported the simultaneous detection of acetaminophen (APAP) and DA at a single walled carbon nanotube (SWCNT)/graphene nanosheet (GNS) hybrid modified films. The films were prepared by sonicating the suspension of a mixture of SWCNT and GNS in DMF solvent and were subsequently dropped onto the GCE surface. The simultaneous determination of both analytes exhibits selectivity properties in which the hybrid film managed to detect APAP from the interference of AA. The peak currents for both analytes increased linearly in the concentration range from 0.1–52.5 μM for APAP and DA. Hence, the detection limit (S/N = 3) was estimated to be 13 nM for APAP and 10 nM for DA.
Besides graphene–CNT composites, GO–CNT composite was also successfully applied for the determination of DA. Although the conductivity of GO, a 2D oxygenated graphene sheet is not as high as graphene, it is regarded as a suitable material for biosensing analysis. GO shows good hydrophilicity properties and could disperse in water due to its abundant hydrophilic functional groups, such as OH, COOH, and epoxides on the basal plane and the sheet edge, all of which can be orthogonally functionalized for biomolecular detection. Moreover, it can also have a good electronic property which carries electron from insulator to low band gap semiconductor depending upon its degree of oxidation. Cheemalapati et al.165 prepared GO/MWCNT nanocomposite by sonicating the mixture of MWCNT and GO into water to produce a homogeneous dispersion. In this work, GO/MWCNT composite was applied for the simultaneous determination of DA and paracetamol (PA). The measurements were made through CV, DPV, and CA as shown in Fig. 14 in which the modified electrode exhibits higher electrocatalytic oxidation of DA and PA in the linear response range from 0.2 to 400 μM and 0.5 to 400 μM with a low detection limit of 22 and 47 nM, respectively.
Fig. 14 (A) CVs of MWCNT/GO nanocomposite film modified GCE (a) without and (b–k) with 200 nM–400 mM of DA and PA containing deoxygenated PBS at 50 mV s−1 scan rate. Inset plot shows the linear dependence of Ipa vs. [DA] and [PA]. (B) DPVs recorded at MWCNT/GO nanocomposite film modified GCE (a) without and (b–n) with 200 nM–400 mM of DA and PA containing deoxygenated PBS at 50 mV s−1 scan rate. Inset plot shows the linear dependence of Ipa vs. [DA] and [PA]. (C) Amperometric i–t response at MWCNT/GO nanocomposite film modified rotating disc GCE upon successive additions of 100 nmol L−1–400 mM of DA into continuously stirred N2 saturated PBS (pH = 7). Applied potential: 0.204 V; inset (upper) shows the calibration curve of Ipa vs. [DA]. Inset (bottom) shows i–t response for each addition of 1 mM of DA. (D) Amperometric responses acquired under similar conditions for successive additions of 200 nM–400 mM of PA. Applied potential of 0.408 V; inset (upper) shows the calibration curve of Ipa vs. [PA]. Inset (bottom) shows i–t response for each addition of 1 mM of PA. Reprinted with permission from ref. 154, Copyrights (2013) Elsevier Publications. |
Another work that simultaneously detect DA and other interference species is done by Yang et al.166 They have developed hexadecyltrimethylammonium bromide (CTAB) functionalized GO/MWCNT modified GCE (CTAB–GO/MWCNT/GCE) as a novel system to construct sensing interface to achieve simultaneous detection of DA, AA, UA, and nitrite (NO2−). For preparation, they have stirred the mixture of graphene and CTAB and then mixed with MWCNT under ultrasonic agitation. In their DPV studies, the linear calibration plots for AA, DA, UA, and NO2− were obtained over the range of 5–300 μM, 5–500 μM, 3–60 μM, and 5–800 μM with LOD of 1, 1.5, 1, and 1.5 μM, respectively. Zhang et al.78 developed a novel biosensor for simultaneous determination of DA, AA, and nitrite (NO2−) based on graphene/poly-cyclodextrin/multiwall carbon nanotubes (CDP–GS–MWCNTs) modified GCE. They have fabricated the biosensor by dispersing graphene sheets (GS) and multiwall carbon nanotubes (MWCNTs) in the mixed solution of cyclodextrin (CD) and cyclodextrin prepolymer (pre-CD), which was subsequently dropped on the surface of the GCE. Based on the CV and DPV techniques, a good separation of the oxidation peak potentials for AA, DA and NO2− was shown and the peak currents increased linearly as the concentrations of AA, DA and NO2− were increased. The linear response range for AA, DA, and NO2− were determined in the ranges of 5 μM–0.48 mM, 0.15–21.65 μM, and 5 μM–6.75 mM, respectively, with the detection limit of 1.65 μM, 0.05 μM, and 1.65 μM. A summary of the various graphene–carbonaceous materials based electrochemical sensor in the detection of DA can be referred in Table 5.
Electrode | Fabrication method | Detection method | Linear range | Limit of detection | Interference | Real sample | References |
---|---|---|---|---|---|---|---|
a CNT: carbon nanotube; Nf: Nafion; HRP: horseradish peroxidase; SWCNT: single walled carbon nanotube; MWCNT: multiwalled carbon nanotube; CTAB: hexadecyl ammonium bromide; poly-CD: poly-cyclodextrin. | |||||||
3D graphene/CNT/Nf/HRP | Two-step CVD | CA | 2–64 μM | 20 nM | — | — | 161 |
Core–shell MWCNT/GO nanoribbons | Microwave | CA | 0.5–50 μM | 80 nM | DA, AA, UA | — | 162 |
RGO/carbon dots | Reduction | DPV | 10 nM–450 μM | 1.5 nM | DA, AA, UA | — | 163 |
SWCNT/graphene NS | Sonication | DPV | 0.1–525 μM | 10 nM | DA, APAP | Human serum | 164 |
GO/MWCNT | Sonication | DPV | 0.2–400 μM | 22 nM | DA, PA | Urine, pharmaceutical sample | 165 |
CTAB/GO/MWCNT | Sonication | DPV | 5–500 μM | 1.5 μM | AA, UA | Urine | 166 |
Graphene/poly-CD/MWCNT | Sonication | DPV | 0.15–22 μM | 50 nM | DA, AA, NO2− | Human urine | 78 |
The applicability in real sample analysis with the graphene–carbonaceous materials was studied by standard addition method. The GO/MWCNT, CTAB/GO/MWCNT and graphene/poly-CD/MWCNT have been employed for the detection of DA in urine. The recovery of DA in urine using GO/MWCNT,165 CTAB/GO/MWCNT,166 and graphene/poly-CD/MWCNT78 were obtained between 98.8 and 104.0, 99 and 110, and 95.0 and 106.6%, respectively. The DA was also determined in human serum sample using SWCNT/graphene NS electrode164 with the recovery falling between 97.1 and 102.1%. Thus, the excellent recoveries of DA was achieved more than 94% validates that this nanocomposite materials remain promising for real sample analysis. Among the reviewed graphene–carbonaceous composite as an electrochemical sensor, the RGO/carbon dots modified electrode showed the lowest LOD of 1.5 nM for DA detection. To date, due to its unique size and shape-dependent of zero-dimensional of CDs which effectively prevents the aggregation of graphene, it should be considered as another significant and important electrochemically active material that may have the potential to be used in sensing applications.
Li et al.77 attempted to study the electrochemical performance of hydrotalcite-like multifunctional materials or anionic clays, named as double hydroxides (LDHs)-based composites and used them for fabricating the electrochemical DA sensor. They have explored a facile two-step procedure to prepare NiAl–LDH/graphene (NiAl–LDH/G) nanocomposite using a conventional co-precipitation process under low-temperature conditions and subsequent reduction of the supporting GO (Fig. 15).
Fig. 15 Schematic illustration of preparing the nanostructured NiAl–LDH/G composite Reprinted with permission from ref. 157, Copyrights (2011) Royal Society of Chemistry. |
The NiAl–LDH/G nanocomposite exhibits highly enhanced electrocatalytic activity in comparison with the electrode modified by the pristine NiAl–LDH. Good linear relationships of electrocatalytic redox peak currents responded to DA were obtained in the DA concentration range from 0.5 to 120 μM (reduction peak current), and also in the concentration range from 80 to 400 μM (oxidation peak current). The detection limits were estimated to be 0.2 and 9.6 μM (S/N = 3) for the reduction and oxidation peak currents, respectively. Another work also reported by Ding et al.,167 in which they investigated the possibility to co-immobilized graphene with synthetic lamellar clay, Laponite. They have developed a Laponite/graphene (Lap/G)-modified GCE for the simultaneous detection of DA, AA, and UA (Fig. 16). The composite was prepared by directly exfoliating graphite with Laponite under mechanical grinding. The well-separated voltammetric peaks of DA, AA, and UA were observed at the Lap/G/GCE as compared with bare GCE in CV as well as in DPV techniques. Through their DPV techniques, the linear response for determination of AA, DA, and UA, ranges from 5 to 1300 μM, 0.5 to 170 μM, and 0.1 to 26 μM, respectively. Therefore, the respective detection limits were determined at 2.2 μM, 0.25 μM, and 45 nM.
Fig. 16 CVs obtained for 1 mM of AA (a), DA (b), and UA (c) individually in 0.1 M PBS at (A) bare GCE and (B) Lap/G/GCE. (C) CVs and (D) DPVs obtained for mixture of 1 mM AA, 0.7 mM DA, and 1 mM UA in 0.1 M PBS (pH 7.0) at bare GCE (a) and Lap/G/GCE (b). Reprinted with permission from ref. 158, Copyrights (2014) Springer. |
As compared to the NiAl–LDH/G, Lap/G reveals a lower LOD in detecting DA. In addition, the reproducibility and stability of both materials are also examined. Lap/G showed better reproducibility of electrode in which the Lap/G could detect around 10 μM DA using five independently prepared electrodes with a RSD of 3.0%, while NiAl–LDH/G detected around 100 μM DA using five independently prepared electrodes with the inter-assay coefficient of variation of 4.2%.
Fig. 17 (A) Schematic illustration for the sonication-assisted preparation of Cu(tpa)–GO, and its application for the simultaneous determination of ACOP and DA. (B) DPVs of ACOP over a concentration range of 1.0 to 100 μM at Cu(tpa)–EGR/GCE in the presence of 20 μM DA in 0.1 M PBS (pH 5.0). (C) DPVs of DA over a concentration range of 1.0 to 50 μM at Cu(tpa)–EGR/GCE in the presence of 50 μM ACOP in 0.1 M PBS (pH 5.0). Insets in (B) and (C) are respectively the linear calibration plots of peak currents (Ipa) versus the concentration of ACOP (CACOP) and DA (CDA). Reprinted with permission from ref. 162, Copyrights (2014) American Chemical Society. |
For real sample analysis, Cu(tpa)–EGR/GCE170 was used to determine DA in diluted urine and serum samples for the recovery of the spiked samples ranged between 98 and 101%, indicating that the material was reliable and sensitive enough for the determination of ACOP and DA in real samples. A summary of the some rare graphene composites with clay, zeolite, and MOF based electrochemical sensor for the detection of DA can be referred in Table 6. Among them, the Cu NPs doped-zeolite A/graphene modified electrode showed the lowest LOD of 45 nM for DA.
Electrode | Fabrication method | Detection method | Linear range | Limit of detection | Interference | Real sample | Ref. |
---|---|---|---|---|---|---|---|
a Cu NPs: copper nanoparticles; MOF: metal organic frameworks. | |||||||
NiAl-layered double hydroxide/graphene | Co-precipitation | CV | 80–400 μM | 9.6 μM | DA, AA | — | 77 |
Laponite/graphene | Mechanical grinding | CV | 0.5–170 μM | 0.25 μM | DA, AA, UA | — | 167 |
Cu NPs doped-zeolite A/graphene | Magnetic stirring and chemical reduction | CV | 0.1–19 μM | 41 nM | DA, AA | — | 168 |
Cu NPs doped-zeolite/graphene | Chemical reduction | DPV | 0.1–19 μM | 41 nM | DA, AA | — | 169 |
Graphene supported chromium carbide | Hydrothermal | SWV | 1–10 μM, 10–100 μM | — | — | — | 81 |
Copper terephthalate MOF-GO | Ultrasonication | DPV | 1–5 μM | 0.21 μM | DA, ACOP | Urine, serum | 170 |
The main challenge faced related with graphene-based materials in electrochemical sensors, is the selectivity towards DA in the presence of other important biological analytes and significant discoveries in this field are expected, due to the increasing need for portable sensors in a wide range of biological and clinical fields. Despite these challenges, the excellent electronic conductivity of graphene-based materials and their ability to combine with other materials makes them ideal candidates for making electrochemical sensor devices. Major fundamental and technological advances have been utilized to enhance the capabilities and improve the detection limit and specific detection of DA in devices fabrication which is easy to operate, reusable, and low-cost fabrication.
Many new graphene-based materials have been investigated, for example graphene, N-doped graphene, functionalized graphene, graphene–metal nanoparticles, graphene–metal oxides, graphene–polymer composites, graphene–carbonaceous composite, graphene–clay composite, graphene–zeolite composite, graphene–metal organic framework have been used for sensor construction to improve their performance of DA sensing. However, only the graphene combined with polymer have shown the capability as a promising material for the electrochemical sensing of DA due to the simple preparation, high sensitivity and selectivity, good reproducibility, and long-term stability. In conclusion, the graphene-based materials and its unique electronic properties make excellent sensing material in the fabrication of DA sensor. In the near future, new developments in the graphene-based composite materials are required in the field of electrochemical sensing of DA with high sensitivity and selectivity for making sensor devices for practical applications. The graphene-based materials and its modified electrode is a versatile system for the detection of DA in the near future.
Footnote |
† These two authors contributed equally to this work. |
This journal is © The Royal Society of Chemistry 2014 |