Ayman H. Kamel*ab,
Abd El-Galil E. Amr*cd,
Abdulrahman A. Almehiziac,
Elsayed A. Elsayedef and
Gaber O. Moustafag
aChemistry Department, College of Science, Sokheer 32038, Kingdom of Bahrain. E-mail: ahkamel76@sci.asu.edu.eg; aamr@ksu.edu.sa
bDepartment of Chemistry, Faculty of Science, Ain Shams University, Cairo 11566, Egypt
cPharmaceutical Chemistry Department, College of Pharmacy, King Saud University, Riyadh 11451, Saudi Arabia. E-mail: mehizia@ksu.edu.sa
dApplied Organic Chemistry Department, National Research Center, Giza 12622, Egypt
eBioproducts Research Department, Zoology Department, Faculty of Science, King Saud University, Riyadh 11451, Saudi Arabia. E-mail: eaelsayed@ksu.edu.sa
fChemistry of Natural and Microbial Products Department, National Research Centre, Dokki 12622, Cairo, Egypt
gDepartment of Peptide Chemistry, National Research Centre, Cairo, Egypt. E-mail: gosman79@gmail.com
First published on 18th August 2021
A simple, cost-effective, portable and disposable paper-based analytical device is designed and fabricated for copper(II) determination. All solid-state ion-selective electrodes (ISEs) for copper and a Ag/AgCl reference electrode were constructed and optimized on the paper substrate. The copper electrodes were built using carbon nano-tube ink as a conductive substrate and an ion-to electron transducer. A suitable polymeric membrane is drop-cast on the surface of the conductive carbon ink window. The copper-sensing membrane is based on newly synthesized macrocyclic pyrido-pentapeptide derivatives as novel ionophores for copper detection. Under the optimized conditions, the presented all-solid-state paper-based Cu2+-ISEs showed a Nernstian response toward Cu2+ ions in 30 mM MES buffer, pH 7.0 over the linear range of 5.0 × 10−7–1.0 × 10−3 M with a limit of detection of 8.0 × 10−8 M. The copper-based sensors exhibited rapid detection of Cu2+ ions with a short response time (<10 s). The selectivity pattern of these new ionophores towards Cu2+ ions over many common mono-, di- and trivalent cations was evaluated using the modified separate solution method (MSSM). The presented paper-based analytical device exhibited good intra-day and inter day precision. The presented tool was successfully applied for trace Cu2+ detection in real samples of serum and whole blood collected from different children with autism spectrum disorder. The data obtained by the proposed potentiometric method were compared with those obtained by the inductively-coupled plasma (ICP) as a reference method. The presented copper paper-based analytical-device can be considered as an attractive tool for point-of-care copper determination because of its affordability, vast availability, and self-pumping ability, particularly when combined with potentiometric detection.
PADs were used to detect heavy metals, which is of great concern due to its toxicity to both humans and animals.15 Copper is one of the most predominant and widely used heavy metals, so its amount in environmental and industrial issues must be under control.16 It is also considered one of the micro-nutrients necessary for the organism because it is involved in the formation of a number of essential proteins. Copper deficiency in the organism leads to various diseases, such as bone deformity in children, osteoporosis in adults, and cardiovascular diseases.17 Despite this, copper is toxic in a high-level concentration and pose a risk. The harmful effect of copper can be seen in several diseases including abdominal pain, nausea, Alzheimer's disease, and Wilson's disease. Furthermore, an increased amount of copper in the body harms the kidneys and liver, and may also contribute to cancer formation.18 Taking the above factors into consideration, controlling the copper content is indispensable. So, the need for a credible, simple, cost-effective, fast and remote method for the determination of copper is of great particular interest in the point-of-care area.
There are several methods of copper determination reported in the literature. They include stripping voltammetery,19–21 fluorimetry,22 inductively coupled plasma/mass spectrometry (ICP/MS),23 atomic flame absorption spectrometry (AAS/flame),24–26 thermoelectric atomic absorption spectrometry (AAS/flameless),27 and chromatography.28 These reported approaches possess some merits such as reasonable selectivity and low-detection limits, but they are sophisticated, time-consuming, require highly expensive instruments, and are not suitable for point-of-care analysis. Therefore, these techniques are not suitable for on-line detection and daily-control of copper content in different fields. These limitations can be overcome by using potentiometric sensors.29–32
All-solid-state potentiometric sensors, wherein a solid-contact layer is inserted between the electrode substrate and an ion-sensing membrane (ISM), act an important role in the detection. These types of electrodes possess good merits such as high potential stability, ease of construction, cost-effective and ability of miniaturization. The application of these electrode design offers fast analysis, short-response time, good selectivity and low-cost analysis.33–35 All of these merits make potentiometric approaches the most favorable approach for Cu2+ assessment. Although there are many solid electrodes for copper measurement in the literature,36–45 they have been applied in environmental analyses. There are no reported sensors for copper determination based on the paper as a solid support for point-of-care purposes.
Herein, a disposable paper-platforms based potentiometric micro-cell was developed for rapid, reliable and accurate assessment of copper ions in whole blood. Novel paper-based copper sensors based on newly synthesized macrocyclic pyrido-pentapeptide derivatives as novel ionophores for copper detection were built and characterized. Then, a novel paper-based solid-state reference electrode is integrated with the constructed copper sensor to build up the potentiometric-cell with an approximately total volume of ∼50 μL. Factors affecting the analytical performance of the presented potentiometric cell were characterized and discussed. The device was successfully applied for accurate determination of copper in whole blood samples collected from autistic children. The data were compared with those obtained by ICP/OES method, and showed no significant difference at 95% confidence interval. The presented potentiometric device opens new avenues for managing copper and implementing paper-based analytical platforms.
All serum and blood samples were collected from different patients have autism disorders and were provided by a local Egyptian hospital.
The miniaturized cell was built up by sandwiching the two electrodes leaving a cavity of ∼50 μL volume using neoprene rubber of 3 mm thick. The constructed paper-based potentiometric device is then connected to the mV/pH meter through the conductive ends of both working and reference electrodes. A simple presentation for constructing the miniaturized cell is shown in Fig. 2.
For sensors based on glassy carbon (GC) substrates, a GC disk electrode (4 mm I.D.) were polished by 0.3 μm γ-Al2O3 and sonicated with ethanol and de-ionized water alternatively and then dried under N2 stream. A piece of PVC tube (1 cm length, 5 mm I.D. and 8 mm O.D.) was inserted at the distal end of the GC substrate. A 10 μL of CNTs ink was coated above the GC disk. After drying, the electrodes were washed with de-ionized water and then dried under a stream of N2 gas. A 100 μL volume of the membrane cocktail (i.e. the same composition as mentioned above) was drop-casted above the CNTs layer. Afterward, the membrane was left to dry until a uniform shape is obtained with good adhesion to the GC substrate.
For electrode optimization and comparison purposes, Cu2+-ISEs based on glassy-carbon (GC-ISE) support were also constructed and their results were compared with the paper-based analytical devices. The GC/Cu2+-ISEs based on ionophore I (sensor III) and ionophore II (sensor IV) showed a Nernstian response with slopes of 29.1 ± 0.5 and 25.6 ± 0.2 mV per decade (30 mM MES buffer, pH 7.0) over the linear range 1.0 × 10−7–1.0 × 10−3 with a limit of detection of 3.4 × 10−8 and 3.4 × 10−8 M, respectively. The obtained results are very similar to those obtained by the presented Cu2+-paper based analytical devices.
The calibration plots for GC/Cu2+-ISEs based on ionophores I and II are shown in Fig. 4. This shows that, there are no significant differences between the presented paper-based analytical devices and the conventional solid-state GC/Cu2+-ISEs in terms of slope-sensitivity and linearity-range. The time-trace response of both paper-based analytical devices and solid-state GC/Cu2+-ISEs based on ionophores I and II are shown in Fig. 3 and 4, respectively. The sensors attained a steady-state potential response in less than 10 s, which is good and reasonable for the use of these devices in de-centralized analysis. A long-term potential stability test showed a potential drift of about 0.3 and 0.25 mV h−1 (16 h) for sensors I and II, respectively, and which is also satisfactory, considering that these devices are intended for a single-short reading. The performance analytical characteristics are summarized in Table 1.
Parameter | Sensor I | Sensor II | Sensor III | Sensor IV |
---|---|---|---|---|
Slope (mV per decade) | 28.6 ± 0.5 | 25.6 ± 0.8 | 29.1 ± 0.6 | 25.6 ± 0.2 |
Correlation coefficient (r2) | 0.999 | 0.999 | 0.999 | 0.999 |
Linear range (M) | 5.0 × 10−7–1.0 × 10−3 | 4.0 × 10−7–1.0 × 10−3 | 1.0 × 10−7–1.0 × 10−3 | 1.0 × 10−7–1.0 × 10−3 |
Detection limit (M) | 8.0 × 10−8 | 6.5 × 10−8 | 3.4 × 10−8 | 3.3 × 10−8 |
Working acidity range (pH) | 4.0–7.5 | 4.0–7.5 | 4.0–7.5 | 4.0–7.5 |
Response time (s) | <5 | <5 | <5 | <5 |
Accuracy (%) | 98.2 | 98.7 | 98.8 | 97.9 |
Trueness (%) | 99.2 | 99.3 | 98.7 | 98.6 |
Bias (%) | 0.6 | 0.4 | 0.9 | 1.1 |
Intra-day precision (%) | 0.8 | 1.3 | 1.1 | 0.9 |
Inter-days precision (%) | 1.1 | 0.8 | 0.9 | 1.2 |
Intra-day and inter-day precision were examined for the presented paper-based analytical devices. 1.0 μg mL−1, internal quality control sample of copper was measured (n = 6). The relative standard deviations were found to be 0.8 and 1.3 for sensors I and II, respectively. Method accuracy was also evaluated by spiking a known Cu2+ amount (0.5 μg mL−1) and found to be 98.2 ± 0.7–98.7 ± 0.6% for sensors I and II, respectively.
The effect of pH on the potential response was tested. The presented sensors showed good stability over the pH range of 4 to 7.5, the electrode-potential does not change by more than ±0.8 mV. At pH values >8 the potential begins to decline at concentrations >10−4 M due to the formation of precipitation of Cu(OH)2 and/or the formation of copper-hydroxo complexes. At pH < 4, the electrode potential increases due to some interferences coming from H+ ions. All subsequent-potentiometric measurements of Cu2+ ions in blood or serum were made as the sample received or in 30 mM MES buffer background of pH 7.0.
Fig. 5 Selectivity pattern for the paper-based electrochemical device based on (A) sensor I and (B) sensor II. |
Fig. 6 displayed the selectivity coefficient values (logKPotCu2+,B) for the most abundant ions and organic compounds that can be found in blood. It was noticed that ionophore I displayed better selectivity towards Cu2+ ions over Hg2+, Cd2+, Ni2+, Co2+ and NH4+ ions than ionophore II. Both ionophores revealed nearly the same selectivity behavior over K+, urea and glucose. Ionophore II exhibited better selectivity towards copper ions over Zn2+, Pb2+ and Na+ ions than ionophore I. From the data presented in Fig. 6, it could be expected that the presented ionophores have high selectivity towards copper ions and its applicability in determining copper content in whole blood without major interferences could be successfully.
Fig. 6 Selectivity coefficient pattern for copper-paper selective electrodes based on ionophores I and II. |
To check the applicability of the presented paper-based potentiometric device for copper determination, six serum samples were collected from different children have autism disorders and then analyzed. Before sample analysis, three standard solutions of copper (e.g., 10.0, 50.0 and 100.0 μg mL−1) were inserted into the potentiometric-cell to build-up the calibration plot. After measuring the standard calibrants, the cell is then washed and the sample is analyzed. The same samples were analyzed with ICP-OES as a reference method-that is normally used in the routine analysis of copper in blood and serum. The results of measuring both serum and blood samples were shown in Tables 3 and 4, respectively. The data confirmed that the analysis was of acceptable accuracy when compared with those obtained by the standard ICP-OES method.
Sample no. | Copper contenta, μg mL−1 | ||
---|---|---|---|
Potentiometry | ICP-OES | ||
Sensor I | Sensor II | ||
a Average of 3 measurements. | |||
Male (age 5–8 years) | |||
1 | 19.4 ± 12 | 17.2 ± 9.0 | 16.2 ± 0.8 |
2 | 57.3 ± 5.0 | 52.2 ± 3.0 | 55.6 ± 0.2 |
3 | 44.5 ± 0.7 | 39.2 ± 6.0 | 42.2 ± 0.1 |
Female (age 4–8 years) | |||
4 | 55.2 ± 0.9 | 51.9 ± 4.0 | 54.4 ± 0.3 |
5 | 63.2 ± 2.0 | 61.5 ± 6.0 | 67.2 ± 0.5 |
6 | 48.1 ± 4.0 | 51.2 ± 3.0 | 45.3 ± 0.1 |
Sample no. | Copper contenta, μg mL−1 | ||
---|---|---|---|
Potentiometry | ICP-OES | ||
Sensor I | Sensor II | ||
a Average of 3 measurements. | |||
Male (age 5–8 years) | |||
1 | 39.2 ± 0.9 | 36.1 ± 4.0 | 35.1 ± 0.2 |
2 | 37.3 ± 0.8 | 32.5 ± 2.1 | 35.6 ± 0.1 |
3 | 40.2 ± 1.7 | 37.2 ± 6.3 | 42.2 ± 0.3 |
Female (age 4–8 years) | |||
4 | 35.3 ± 1.9 | 31.2 ± 4.4 | 34.2 ± 0.1 |
5 | 33.4 ± 3.3 | 31.6 ± 1.4 | 37.5 ± 0.3 |
6 | 43.3 ± 3.6 | 41.4 ± 2.1 | 40.4 ± 0.2 |
Ionophore | Type of electrode | Solid contact transducer | Slope, mV per decade | Detection limit, M | Linear range, M | Ref. |
---|---|---|---|---|---|---|
(4-Phenyl-11-decanoyl-1,7-dithia-11-aza-cyclotetradecane-4-sulfide) | Pt micro-electrode | PPy [3,3′-Co (1,2-C2 B9 H11)2] | 29.5 ± 1 | 5.6 × 10−7 | 1 × 10−6–1 × 10−2 | 36 |
Copper ionophore (IV) | GC | Graphene/7,7,8,8-tetracyano-quinodimethane | 30.5 ± 0.05 | 8 × 10−10 | 1 × 10−9–1 × 10−2 | 37 |
Copper ionophore (II) | Graphite powder/resin | Three-dimensional graphene sponge | 28.9 ± 0.7 | 2.5 × 10−9 | 1 × 10−8–7.9 × 10−4 | 38 |
Phytic acid/Ag composite | Gold substrate | Ag nanoparticles | 31.1 ± 1.8 | 2.7 × 10−6 | 1 × 10−5–1 × 10−3 | 39 |
2-Mercapto-benzoxazole | Screen-printed | PEDOT/PSS | 28 | 3 × 10−7 | 1 × 10−6–1 × 10−2 | 40 |
5-Sulfosalicylic acid | Pencil graphite | Polypyrrol | 29.6 ± 0.3 | 5.4 × 10−6 | 1 × 10−5–1 × 10−1 | 41 |
Copper ionophore (ETH 1062) | Gold wire | PEDOT/PSS | 28.1 ± 1.8 | 4 × 10−8 | 2.5 × 10−7–2.5 × 10−4 | 42 |
2-(1′-(4′-(1′′-Hydroxy-2′′-naphthyl)methyleneamino)butyl iminomethyl)-1-naphthol | Graphite powder/resin | MWCNTs | 29.7 ± 0.2 | 5.5 × 10−9 | 1 × 10−8–1 × 10−3 | 43 |
Diphenylisocyanate bis (acetylacetone)ethylenediimine | Graphite powder/resin | MWCNTs | 29.4 ± 0.4 | 2.4 × 10−9 | 1 × 10−8–1 × 10−3 | 44 |
N-Hydroxy succinamide | Graphite powder/resin | — | 37.5 | 4.4 × 10−6 | 1 × 10−4–1 × 10−2 | 45 |
Macrocyclic pyrido pentapeptide derivative 1 (ionophore I) | Paper based modified with CNTs | Carbon nanotubes ink (CNTs) | 28.6 ± 0.5 | 8 × 10−8 | 5.7 × 10−7–1 × 10−3 | This work |
Macrocyclic pyrido pentapeptide derivative 2 (ionophore II) | 25.6 ± 0.8 | 6.5 × 10−8 | 4 × 10−7–1 × 10−3 |
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