Tushar
Kant
*a,
Kamlesh
Shrivas
*b,
Ankita
Tejwani
b,
Khushali
Tandey
b,
Anuradha
Sharma
c and
Shashi
Gupta
c
aShaheed Kawasi Rodda Pedda, Govt. College Kuakonda, Dantewada-494552, CG, India. E-mail: tusharkant40@gmail.com
bSchool of Studies in Chemistry, Pt. Ravishankar Shukla University, Raipur-492010, CG, India. E-mail: kshrivas@gmail.com
cDepartment of Zoology, Govt. Nagarjuna P.G. College of Science, Raipur-492010, CG, India
First published on 22nd November 2023
The need for precise determination of heavy metals, anions, biomolecules, pesticides, drugs, and other substances is vital across clinical, environmental, and food safety domains. Recent years have seen significant progress in portable colorimetric chemical sensing devices, revolutionizing on-the-spot analysis. This review offers a comprehensive overview of these advancements, covering handheld colorimetry, RGB-based colorimetry, paper-based colorimetry, and wearable colorimetry devices. It explores the underlying principles, functional materials (chromophoric reagents/dyes and nanoparticles), detection mechanisms, and their applications in environmental monitoring, clinical care, and food safety. Noble metal nanoparticles (NPs) have arisen as promising substitutes in the realm of sensing materials. They display notable advantages, including heightened sensitivity, the ability to fine-tune their plasmonic characteristics for improved selectivity, and the capacity to induce visible color changes, and simplifying detection. Integration of NPs fabricated paper device with smartphones and wearables facilitates reagent-free, cost-effective, and portable colorimetric sensing, enabling real-time analysis and remote monitoring.
Numerous analytical methods are utilized in diverse applications for identification and examination of metals, biomolecules, toxicants, and various other substances. For metal detection, methods such as atomic absorption spectroscopy (AAS),6 inductively coupled plasma-atomic emission spectroscopy (ICP-AES),7 ICP-mass spectrometry (MS),8 fluorimetry,9 and electroanalytical methods10 are commonly utilized. In the analysis of biomolecules, pesticides, drugs, and volatile organic compounds (VOCs) from environmental, clinical, food, and industrial samples, techniques like fluorimetry,11 electroanalytical methods,12 high-performance liquid chromatography (HPLC),13 gas chromatography (GC),14 liquid chromatography-mass spectrometry (LC-MS),15 and gas chromatography-mass spectrometry (GC-MS)16 are widely used. The selection of specific methods depends on the nature of the substances being analyzed, the desired level of sensitivity and accuracy, and the particular application requirements. AAS, ICP-AES, ICP-MS, GC, HPLC, GC-MS, LC-MS, fluorimetry, and electroanalytical methods exhibit high sensitivity for detecting various chemical substances; however, they can be expensive, require trained personnel, and may not be applicable at the sample sources.
Among the analytical methods discussed, colorimetry, often referred to as spectrophotometry, distinguishes itself as a straightforward and easily accessible approach for identifying a wide range of chemical compounds. The fundamental principle of colorimetry centers around the quantitative analysis of chemical substances in a solution. This analysis is achieved by measuring the absorption of light, which occurs when colored complexes are formed through a chemical reaction between chromophoric reagents or dyes and the target analyte.17–20 Indeed, this method have its drawbacks. One major limitation is the necessity for specific chromophoric reagents or dyes tailored to the target analyte, which can be time-consuming and expensive to develop or acquire. Moreover, the relatively large volume of solution required (approximately 3–5 mL) adds to the overall cost of the analysis. Furthermore, it is possible to encounter selectivity challenges, which can create difficulties in accurately differentiating the desired analyte from other substances within the solution. These considerations highlight the need for alternative analytical approaches that can overcome these limitations and provide more cost-effective and selective measurements.21,22
Noble metal nanoparticles (NPs) such as gold (Au), silver (Ag) and copper have gained significant attention as colorimetric sensing probes in place of traditional chromophoric reagents or dyes. These NPs exhibit exceptional sensitivity due to their strong localized surface plasmon resonances (LSPR), allowing for the detection of minute concentrations of analytes with high precision. The tunable plasmonic properties of noble metal NPs enable tailoring their sensing capabilities to specific analytes, enhancing selectivity. Their color changes are visually detectable, obviating the need for complex instrumentation and making colorimetric sensing accessible in various settings. Moreover, the stability and photostability of noble metal NPs ensure reliable and reproducible results over time.23–26 Their biocompatibility, particularly in the case of Au and AgNPs, expands their utility to biomedical applications. Surface functionalization facilitates the development of targeted and specific sensing platforms, while the cost-effectiveness of synthesis methods allows for mass production and practical implementation. This reagent-free and cost-effective nature of NP-based colorimetric sensing makes it a promising and versatile tool for the detection of a variety of chemical substances.
Smartphone and wearable colorimetric detection refers to the use of smartphones or wearable devices to perform color-based analyses for detecting and measuring chemical substances in various applications. Smartphones and wearable electronics now come with high-resolution cameras and powerful image processing tools because of advances in technology. It now becomes possible to use these gadgets as easily transportable and available equipment for colorimetric analysis. Images of the reaction mixture or sample are often taken, and then using specialized software or mobile applications, the color changes are analyzed and turned into quantitative data.27–30 The integration of colorimetric detection with smartphones and wearables offers several advantages. Firstly, it eliminates the need for bulky and expensive laboratory equipment, making it more cost-effective and accessible, particularly in resource-limited settings or for on-the-spot testing. Additionally, it allows for real-time analysis and remote monitoring, enabling rapid response and data sharing. Smartphone and wearable colorimetric detection finds applications across diverse domains, encompassing medical diagnostics (such as the identification of biomarkers for diseases), environmental surveillance (like assessing water quality), ensuring food safety (including the detection of contaminants), and various other areas. As technology continues to advance, the potential for these devices to revolutionize on-the-go colorimetric detection and data collection is promising. However, it is essential to address challenges such as calibration, accuracy, and standardization to ensure reliable and precise results.31–36
In conclusion, this review provides details on how the addition of NPs, chromophores, and probes has increased the sensor capacity for the determination of chemical substances. This review article provides explanation of improvements in portable colorimetric chemical sensing devices. It also details how the research combination of paper-based sensor systems, smartphone compatibility, and portable techniques have all deeply changed the field of chemical sensing. They hold great potential for various uses, such as environmental surveillance, industrial applications and point-of-care medical testing since these portable sensors associate these various technologies to give rapid sensitive and inexpensive detection methods. For scientists and engineers who are interested in the most recent developments in this field, this review will be a great resource.
Fig. 1 A portable handheld colorimetry device for the self-referenced solution-based determination of the analyte. |
Fig. 2 (a–c) show the portable handheld RGB-based colorimetry device for the self-referenced solution-based determination of the water content in ethanol [this figure has been reproduced from ref. 40 with permission from Elsevier Sciences, copyright 2020]. |
Fig. 3 Design and development of a smartphone-assisted paper-based portable colorimetric device for the on-site detection of the analyte [this figure has been reproduced from ref. 44 with permission from Springer Nature, copyright 2020]. |
Vellingiri et al.49 demonstrated the identification of nitrite ions (NO2−) in water and wastewater by employing fuchsin dye as a colorimetric indicator. They applied basic fuchsin (BF) onto Whatman filter paper, and observed that when NO2− ions at various concentrations ranging from 0.005 to 9.2 mg L−1 were introduced to the BF-coated paper, a noticeable color transition from pink to colorless ensued as a result of diazotization. This color change offered a visible indication of the presence of NO2− ions. The LOD value was calculated to be 0.005 mg L−1 and the change in color intensity was measured, and the calculated RGB value using an RGB analyzer which is shown in Fig. 4 corresponded to the concentration of the analyte present in the sample. Chen and group50 presented a colorimetric sensing probe using Nile red, zinc tetraphenyl porphyrin (Zn-TPP), and methyl red dyes to monitor the aging and spoilage of chicken at different temperatures. The sensing principle relies on the reaction of these dyes with the emanating gas released from chicken meat. The sensor was constructed with vapor-sensitive dyes enclosed in resin microbeads, arranged in a barcode sequence on an affordable paper substrate. Each barcode pattern exhibits distinct colors, and the RGB values of these patterns can be calculated using a smartphone.
Fig. 4 Systematic representation of fuchsin dye-based nitrite ion (NO2−) detection in real water and wastewater samples [this figure has been reproduced from ref. 49 with permission from Elsevier Sciences, copyright 2019]. |
Liu and coworkers51 demonstrated a paper sensor based on a dye/dye-Cu-MOF (metal–organic framework) for detecting mildewed wheat. Four dyes, namely bromocresol purple, bromophenol blue, bromophenol red, and bromoxylenol blue, were employed to prepare the dye/dye-Cu-MOF complex. When mildewed wheat is introduced into a sealed container, it emits a variety of volatile gases that result in the deprotonation of phenolic hydroxyl groups. The existence of bromine atoms speeds up the process of electron extraction, and the addition of Cu2+ has the potential to give rise to ion associates. The color change of the sensor depends on whether the dyes gain or lose electrons, and the RGB values are analyzed accordingly.
Despite their advantages, molecular sensing probes using chromophoric reagents and organic dyes may have intrinsic drawbacks such as photobleaching susceptibility, low stability, and possible toxicity. Additionally, the design and synthesis of highly specific probes can be challenging and may require extensive optimization for different target molecules. On the other hand, because of their distinct features, NPs provide a convincing substitute as probes for portable colorimetric sensing applications. Nanomaterials overcome the drawbacks of conventional chromophores and dyes with their enhanced sensitivity, excellent stability, and adjustable properties. They are also perfect for mobile and field-based sensing applications because to their tiny size, which makes it simple to integrate them into portable equipment.
For example, Cho et al.53 reported a portable colorimetric sensing method utilizing AuNPs as a sensing probe to detect Cd2+ in potable water samples. The study involved the synthesis of glutathione-functionalized AuNPs (AuNPs-GSH) through a citrate reduction approach, which were then deposited on a flexible polyethylene terephthalate (PET) substrate using polyvinyl pyrrolidone (PVP) as a binder. The study demonstrated that AuNPs-GSH exhibited aggregation in aqueous environments upon exposure to Cd2+, resulting in a distinct visual transformation of the solution color from red to blue. The aggregation is facilitated by the chelation of Cd2+ ions to the glutamyl amino groups of GSH anchored onto the surface of AuNPs. In another example, Zhang and coworkers54 developed a synthesis process to prepare vinyl phosphonic acid (VPA) functionalized AuNPs with a distinctive wine-red color using the NaBH4 reduction method. They established a smartphone-based colorimetric sensing technique to detect uranyl ions (UO22+) in water samples. When AuNPs-VPA were introduced to the UO22+ sample, the AuNPs underwent a color shift, transitioning from a wine-red shade to blue, and the smartphone application ‘photo-matrix’ measured the intensity of this color change. This method allowed for the determination of UO22+ at a minimum concentration of 2 μM.
Duenchay et al.55 developed flexible sensing strips for the detection of vitamin B1 in urine samples. They achieved this by depositing AuNPs on a transparency sheet. AuNPs were synthesized using a citrate reduction method without the need for further modifications and were stabilized by the negatively charged citrate ions. The principle for estimating the vitamin B1 concentration is based on the aggregation of AuNPs, which occurs as a result of electrostatic interactions between vitamin B1, carrying a positive charge, and citrate ions with a negative charge, responsible for stabilizing the AuNPs. As a consequence, this led to a noticeable color change in the transparency paper sheet, which was then processed using the ImageJ application on a smartphone to generate RGB colors for quantitative measurement of B1 in urine samples.
Gan and coworkers56 developed an on-site colorimetric detection method for Cd2+ in water, employing aptamer-functionalized AuNPs (AuNPs-aptamer) as a sensing probe. The researchers utilized a self-developed smartphone-based application to optimize the color change in the solution. In this approach, the stability of AuNPs-aptamer in the presence of NaCl can be attributed to the repulsion between the negatively charged aptamers coating the NPs, which prevents their self-aggregation. However, upon the addition of Cd2+ to the AuNPs-aptamer solution, the aptamer exhibited a higher affinity for Cd2+, resulting in self-elimination from the AuNPs. The color of the solution was changed, and the procedure and mechanism are shown in Fig. 5. An image processing software was used for the extraction RGB intensity of the paper substrate for quantitative estimation of the target substance. The LOD value calculated for Cd2+ was 1.12 μg L−1 in the water sample, which is less than the permissible limit (5 μg L−1) of Cd2+ in drinking water.
Fig. 5 Mechanism of the detection of Cd2+ in drinking water using an AuNP-aptamer based sensing probe [this figure has been reproduced from ref. 56 with permission from Elsevier Sciences, copyright 2020]. |
Esfahani and group57 presented an innovative technique for quantifying phosphate (PO43−) ions through the use of a stable Eu3+ tablet-based method, in which AuNPs stabilized with mercaptoacetic acid (MAA) played a pivotal role. In this method, Eu3+ is encapsulated within a dextran matrix, forming a tablet-shaped structure. Subsequently, this dextran-encapsulated Eu3+ tablet was dissolved in the water sample intended for analysis, and AuNPs-MAA was introduced. As a result of this process, a distinctive color shift, transitioning from blue to red, was observed. This transformation occurred due to the surface plasmon resonance (SPR) effect, brought about by the aggregation of AuNPs in the presence of PO43−. Rajamanikandan et al.58 introduced a fast, straightforward, and user-friendly approach for the sensitive detection of cysteine (Cys) by utilizing AuNPs functionalized with β-cyclodextrin (β-CD). The high binding affinity of Cys's thiol group to the surface of AuNPs-β-CD, leading to the formation of Au–thiol bonds, resulted in aggregation and observable colorimetric changes.
Thus, AuNPs serve as effective tools for portable colorimetric sensing, offering stability and ease of production. They are utilized in various studies for rapid and user-friendly detection of substances, although the cost of synthesizing AuNPs remains a limiting factor. Nevertheless, AuNP-based sensors hold promise for point-of-care diagnostics and environmental monitoring, with ongoing efforts to address associated challenges.
For example, Monisha and coworkers60 proposed a chemical reduction method to prepare AgNPs for the detection of Hg2+. The researchers utilized NaBH4 and PVP as the reducing and capping agents, respectively, leading to the synthesis of PVP-capped AgNPs. These NPs were printed on filter paper using the inkjet printing method. Subsequently, when Hg2+ solution was dropped onto the printed paper substrate and allowed to stand for a few min, a transition in color from yellow to colorless took place, and the alteration in color intensity was quantified using ImageJ software on a smartphone. The approach for the synthesis of AgNPs-PVP and the mechanism for colorimetric detection of Hg2+ are shown in Fig. 6(a–f).
Fig. 6 Systematic representation of the development of an AgNPs-PVP-based portable colorimetric sensor. (a) Synthesis of AgNPs-PVP. (b) Printing of AgNPs in filter paper. (c) Pipetting Hg2+ in an AgNP sensing probe. (d) Image captured using a smartphone. (e) RGB value analyzed using ImageJ software. (f) The result as a calibration curve [this figure has been reproduced from ref. 60 with permission from Elsevier Sciences, copyright 2021]. |
Shrivas et al.44 introduced an innovative technique for synthesizing AgNPs to facilitate on-site detection of Fe3+ in both biological and environmental samples. Different capping agents, such as bare AgNPs, AgNPs-CTAB, AgNPs-CPC, and AgNPs-citrate, were utilized for AgNP synthesis, among which citrate capped NPs were found to be suitable for the detection of Fe3+. The NPs impregnated on paper showed yellow color and the introduction of Fe3+ resulted in discoloration due to the aggregation of AgNPs. This approach exhibited a favorable relative recovery range of 91.3%–95.0% and showcased its capability for the selective determination of total iron in both water and blood plasma samples, as confirmed by interference studies.
Another work by Shrivas and colleagues61 presented a study showcasing AgNP-based paper analytical devices for detecting Pb2+ in real water samples. The researchers synthesized AgNPs-PVA through a reduction process using NaBH4. After AgNPs and Pb2+ were immobilized on glass fiber paper, a noticeable color shift occurred, linked to the aggregation caused by the displacement of the stabilizing agent, prompted by the interaction between Pb2+ ions and PVA molecules. The change in color intensity on the paper was assessed by employing a smartphone and ImageJ software for the quantification of the target analyte.
The synthesis of NPs often involves the chemical reduction process, which employs potentially toxic chemicals like NaBH4 and hydrazine. This raises significant environmental and public health concerns. To address this issue, a green synthesis approach62 can be adopted for NP preparation, utilizing natural sources like plant bark, leaves, and seeds as reducing agents. Previous research has already explored the use of green synthesis to produce AgNPs for portable colorimetric sensing applications. For example, Mavaei et al.63 utilized Achillea wilhelmsii (AW) extract to synthesize AgNPs for analysis of Hg2+ using paper colorimetry. The AgNPs-AW were manually deposited on the paper substrate, and the analyte was added dropwise. The color change from brown to colorless was easily observable by the naked eye. The color transition occurs due to the introduction of Hg2+ ions into the AuNPs, leading to the formation of amalgam (Hg–Ag) and subsequent aggregations. The method achieved a low LOD value of 28 nM for detecting Hg2+. In another example, Infant and group64 presented a greener approach for synthesizing AgNPs using Trigonella foenum (Linnaeus) plant extract, resulting in 27.24 nm cubic-shaped AgNPs. The AgNPs were sprayed onto a paper substrate, and the Hg2+ analyte was dropwise added to the AgNP-coated paper. The color change was observed without the need for a spectrometer, allowing for simple and direct visual detection. Kahandal and coworkers65 demonstrated the development of a portable colorimetric sensor for instant paper-based Hg2+ detection. This sensor utilized green-synthesized AgNPs and was assisted by a smartphone for quick and efficient results. In this article, AgNPs were synthesized from the flower extract of Acacia nilotica using a hydrothermal process. Various concentrations of Hg2+ from 50 to 450 μM were tested. This sensor exhibits excellent selectivity for Hg2+ as it was successfully tested alongside twelve other heavy metals simultaneously, demonstrating its ability to specifically detect Hg2+ among a range of potential interfering substances.
For instance, Chandran and colleagues68 reported the preparation of curcumin functionalized CuNPs (CuNPs-curcumin) for clinically diagnosing Na+ ions in both blood serum and urine. CuNPs functionalized with curcumin were produced through a direct chemical reduction process utilizing NaBH4 as the reducing agent and curcumin as the stabilizing component. The CuNPs-curcumin were deposited onto cellulose paper strips, and upon immersion in a Na+-containing analyte, a color change from pale yellow to dark yellow occurred. The sensing mechanism was elucidated by examining the interaction between Na+ ions and curcumin molecules, leading to the formation of a coordination complex and subsequently causing the aggregation of AuNPs. The RGB color intensity was measured using ImageJ software with a smartphone. Similarly, Ma and Coworkers69 introduced mercaptosuccinic acid (MSA)-stabilized CuNPs for enzyme-free portable colorimetric sensing of H2O2 and uric acid (UA) in human urine samples. When UA or H2O2 molecules came into contact with small CuNPs-MSA, aggregation was induced, resulting in the formation of a violet color. This color change occurred due to the displacement of MSA from the surface of CuNPs. The concentration of UA and H2O2 was measured by calibrating the change in color intensity using a handheld colorimeter. Furthermore, Ilgar and colleagues70 demonstrated a green synthesis of CuO NPs through sonicaion process. Herein, maca extract-coated CuO synthesized for the detection of dopamine is shown in Fig. 7(a–f). In this article, a smartphone-assisted paper-based colorimetric sensor was developed. The value of LOD calculated was 16.9 nM for dopamine detection using CuO-Maca NPs as a sensing probe.
Fig. 7 CuO-Maca NP-based portable colorimetric/electrochemical sensing of dopamine using the paper-based smartphone sensing technique. (A) Synthesis of CuO-Maca by a sonication method. (B) Image of Maca-CuO NPs. (C) Characterization of CuO-Maca. (D) Antibacterial activity check using CuO-Maca. (E) Smartphone-assisted colorimetric sensing. (F) Portable electrochemical sensing of dopamine [this figure has been reproduced from ref. 70 with permission from Elsevier Sciences, copyright 2022]. |
Karakus et al.71 presented a study involving Camellia sinensis polyphenol-capped copper oxide nanoparticles (CuO-PPS NPs) for portable colorimetric sensing of NH3. The researchers utilized a smartphone-based colorimetric method with a paper strip sensor. The CuO-PPS NPs were soaked into the paper substrate and allowed to dry. Upon exposure to NH3, a color change was observed and captured using the smartphone's built-in camera, and the RGB value was calculated using the smartphone for quantitative analysis. Hence, investigating CuNPs for RGB-based colorimetric sensing reveals a cost-effective and versatile solution with easy analyte aggregation. However, CuNPs’ susceptibility to oxidation presents a challenge, necessitating stabilization techniques. Successful functionalization of CuNPs for specific applications, like ion diagnosis and molecule detection, highlights their adaptability and potential in colorimetric sensing.
Moreover, BNPs can be synthesized using both chemical reduction and green synthesis approaches for portable colorimetric sensor applications. For example, Bordbar and colleagues75 designed bimetallic NPs composed of Au and Ag to detect ignitable liquids in gasoline. They employed a green synthesis approach with lemon juice and orange juice acting as reducing agents, alongside a chemical reduction process exploited the utilization of gallic acid, citrate ions, ascorbic acid, etc. When exposed to sample vapors, the sensor underwent aggregation, leading to discernible color alterations in the NPs. These alterations in color were documented with a scanner, ultimately producing unique colorimetric maps for each analyte, facilitating the identification of the tested fuels.
Thus, BNPs enhance portable colorimetric sensing by improving sensitivity, selectivity, and response times. BNPs enable on-site analysis and can be synthesized using eco-friendly methods. Their practical applications, such as pesticide detection and food spoilage monitoring, make them a promising tool for a wide range of applications.
Fig. 8 Portable handheld colorimetric detection of phosphate [this figure has been reproduced from ref. 37 under open access article in terms of the Creative Commons CC-BY license]. |
Srivastava and coworkers76 developed a portable spectrometer designed for the measurement of Fe3+ and Cu2+ in drinking water samples. The spectrometer consists of a radiation source using a white LED and a spectral sensor (AS7262) designed for the detection of visible radiation. An energy-efficient wireless embedded platform operating at sub-GHz frequencies was engineered and connected to both the light source and detector. The accuracy and precision of the device was tested using the commercially available HANNA colorimetric instrument. Inamori and colleagues77 developed a wearable colorimetric device for real-time monitoring of jaundice and vital signs. The incorporation of four LEDs in the device measures the SpO2 levels, bilirubin and heart rate in neonates. The fabrication of a polydimethylsiloxane (PDMS) lens in the device amplifies the signals reflected from LEDs. A smartphone and a personal computer can be used as processing and display systems. Kumar and coworkers78 reported the use of a handheld device for As3+ analysis in water samples. In their approach, As3+ was mixed with KIO3 to undergo an oxidation reaction, converting As3+ to As5+ and liberating iodine. This reaction caused the color to change from red to colorless. A calibration plot was drawn to determine the unknown concentration of As3+ based on the observed color change. Yu and team79 developed a cost-effective, wireless, and handheld spectrophotometer designed for the colorimetric analysis of DNA, BSA, and Cu2+ metal ions. They assembled various components using 3D printing technology. The device can scan samples within the 405–690 nm wavelength range, and an Android application, connected via bluetooth, was employed for measuring the absorbance of solutions. The device demonstrated sensitivity on par with that of a commercial spectrophotometer. This device finds practical utility in analyzing fluid samples across a range of fields, environmental, biological and clinical diagnostics.
These studies are of significant importance as they introduce compact and cost-effective technologies for chemical analysis, enabling on-site assessments without the need for extensive laboratory setups. This accessibility to rapid and accurate chemical sensing has broad implications, ranging from ensuring safe drinking water quality to monitoring vital signs in healthcare, ultimately enhancing our ability to address environmental, biological, and clinical challenges efficiently and affordably.
Fig. 9 Solution-based portable RGB analysis using a smartphone [this figure has been reproduced from ref. 41 with permission from Willey Sciences, copyright 2017]. |
Šafranko and team80 developed an image processing software for quantification of chemical substances through digital colorimetric imaging. Here, digital imaging devices such smartphones and cameras are exploited for taking the images of CuSO4 (blue), CoSO4 (red), KMnO4 (purple), and NiSO4 (green) solutions of different concentrations. The image processing software ColorX was used to calculate the concentration of unknown colored solution using RGB valued through measurements. This approach holds significant educational value for students, serving as a valuable tool and a learning model. In a study led by Rajamanikandan et al.,81 they illustrated a colorimetric detection technique for Cr3+ in environmental water using smartphones. The analysis relied on utilizing the RGB color ratio for Cr3+ analysis in the water samples. In this process, the introduction of Cr3+ into mercapto-5-methyl-1,3,4-thiadiazole (MMT)-modified AuNPs resulted in the release of MMT from the NP surface, forming a distinctive colored complex with the target analyte, which was subsequently measured using a smartphone.
RGB-based colorimetry is pivotal for its ability to provide quick and on-the-spot detection of a wide range of substances, from contaminants to analytes, using portable and user-friendly devices. This technology offers rapid results without the need for complex laboratory setups, making it highly adaptable for applications in environmental monitoring, medical diagnostics, and industrial safety.
Shrivas and co-workers82 engineered a portable colorimetric detector that operates with smartphones to sense As3+ in water and soil samples. Their method involved employing sucrose-capped AuNPs as a nanoprobe and depositing 50 μL of these NPs onto wax treated filter paper. Following this, different concentrations of As3+ were introduced for analysis, and the alterations in color intensity were quantified using ImageJ software. A calibration curve was then constructed to interpret the results. Dong et al.83 presented a novel smartphone-based sensing approach for detecting PO43− in food samples, based on color changes resulting from the aggregation and anti-aggregation of PVP-modified AgNPs induced by Pb2+ and PO43−, and measurements were made using the ‘Color-Assist’ app on a smartphone. Wang and coworkers84 introduced a smartphone-based plasmonic sensing system coupled with image processing, illustrating two colorimetric biochemical sensing concepts based on nano plasmonic phenomena, significantly improving the LOD, and demonstrating its potential for point-of-care and early kidney disease detection in urine testing. Dong and group85 proposed a smartphone-based colorimetric detection approach for thiosulfate (S2O32−), utilizing tannic acid-stabilized AgNPs mixed with different concentrations of S2O32−, and recording color intensity changes using the ‘Color-Assist’ app, effectively estimating unknown concentrations of S2O32− in agricultural samples. Li and group86 demonstrated a smartphone-based colorimetric sensing approach for detecting ascorbic acid (AA) in tropical fruits. Here a material called Fe-single atom non-enzyme (Fe-SAN), synthesized from green tea leaves and NaH2PO4, resulted in a change in the color of 3,3′,5,5′-tetramethylbenzidine from colorless to blue. The introduction of AA effectively prevented this color transformation of the dye. This mechanism offered a better LOD, facilitating the estimation of AA concentrations in a variety of fruits. Choudhary et al.87 demonstrated a paper-based colorimetric sensor utilizing brilliant green (BG) as a probe for detecting phosphate ions in drinking water. A Whatman filter paper strip was prepared using a dip coating method, ultrasonicated with the ‘Tween-80’ surfactant, and soaked with an acidified ammonium molybdate solution. BG solution was then deposited on the paper strip. In the absence of phosphate ions, the probe appeared as a pale-yellow color. Subsequently, different concentrations of phosphate ions from 13.6 to 0.27 mg L−1 were added at various pH levels, and the color change was measured using ImageJ software. The LOD value was calculated 0.07 mg L−1. High concentrations led to a color change to green, while low concentrations resulted in a loss of color intensity and a shift to yellow, as illustrated in Fig. 10.
Fig. 10 A paper-based colorimetric sensor formulated with ammonium molybdate and BG for the detection of phosphate ion in drinking water [this figure has been reproduced from ref. 87 with permission from Elsevier Sciences, copyright 2021]. |
Firdaus and colleagues88 developed a paper-based sensor using stabilized AgNPs for rapid analysis of Hg2+ ions. A hydrophobic ink and nanomaterials (NMs) were printed on paper substrates, resulting in a color change from pale yellow to colorless when mercury ions were added. The RGB intensity change was measured using ‘MATLAB’ software, and a calibration curve was plotted to determine unknown concentrations of analytes. Zhu and group89 demonstrated a paper-colorimetric strip coated with polysulfobetaine methacrylate (pSBMA) for the determination of three pesticides (cypermethrin, profenofos, and chlorpyrifos). The paper sensor was developed by depositing the zwitterionic polymer pSBMA on a glass substrate using PDMS, with cellulose filter paper as the selected material. When pesticides were added to this paper sensor, a color change was observed, and the color intensity was optimized using ‘ImageJ’ software, resulting in LOD values of 0.235 mg L−1 for chlorpyrifos, 4.891 mg L−1 for profenofos, and 4.053 mg L−1 for cypermethrin. Kong et al.90 designed a paper sensor based on ZnFe2O4 magnetic NPs (ZnFe2O4 MNPs) for colorimetric detection of bisphenol A. The sensor's adsorption capacity was evaluated using an adsorption isotherm model, where ZnFe2O4 MNPs and paper were wrapped with a molecular imprinted polymer (MIP). The sensor exhibited a gray intensity that corresponded to the concentrations of bisphenol-A, possessing a LOD of 6.18 nM, making it suitable for environmental monitoring, security inspection, and complex matrices. Ratnarathorn and colleagues91 demonstrated a paper-based analytical device (PAD) designed for the colorimetric detection of Cu2+ in water samples. The sensing probe, consisting of thiol-modified AgNPs on a paper substrate, displayed a transition in color, shifting from pale yellow to shades of orange and green-brown upon the introduction of Cu2+. The color intensity change was measured using ‘Adobe Photoshop CS2’ software, and a calibration curve was plotted, resulting in a LOD value of 0.5 μg L−1 observed by the naked eye. Silva and colleagues92 introduced a new sensing strategy utilizing a paper substrate for the identification of phenacetin in cocaine samples. The proposed approach utilizes white office paper with detecting zones created using wax printing technology. A chromophoric material (1,2-naphthoquinone-4-sulfonate) was spotted on the paper, and upon adding an alkaline cocaine sample, resulting in a distinct color transition from colorless to violet. The color alteration was quantified using ‘GIMP2’ software, and a calibration curve was generated for varying concentrations of cocaine, yielding a LOD of 3.5 μg L−1. Zhang et al.93 demonstrated a paper-based sensor for the recognition of biomarkers related to H2O2, using glucose oxidase as an example. In the presence of H2O2, KI can catalyze the oxidation of tetramethylbenzidine to colorize the paper-based sensing region. The color intensity was photographed using a scanner and the change in the intensity of RGB value was analyzed using Adobe Photoshop, making it an affordable, ecologically safe, and simple technique for testing H2O2-related biomarkers at the point of care. Paper-based colorimetric devices are well-suited for point-of-care applications in resource-constrained environments due to their user-friendliness, affordability, and disposability.94 These advancements drive innovation in portable colorimetric sensing, expanding its potential applications in healthcare, environmental monitoring, food safety, and other domains.
Paper-based RGB/grey scale colorimetry, when combined with smartphones or portable sensing devices, offers a transformative approach to portable and cost-effective colorimetric sensing for measuring diverse chemical substances. Its user-friendly and disposable nature, along with real-time data capture, makes it a valuable tool for addressing critical challenges in healthcare, environmental protection, and food quality assurance. These studies demonstrate its practical applications in fields like environmental monitoring, healthcare, and food safety, particularly in resource-limited settings.
Fig. 11 A BCG sol–gel dye-spotted cellulose substrate-based colorimetric wearable skin surface pH sensor. (a) Three layers of the sensor, (b) the sensor tapped on a palm and (c) the sensor tapped on the wrist [this figure has been reproduced from ref. 96 under open access article in terms of the Creative Commons CC-BY license]. |
Hwang and colleagues97 introduced a flexible wearable H2 gas sensor based on PdO@ZnO with a polyacrylonitrile composite, formed through an electrospinning process on polyacrylamide and coated with polydimethylsiloxane, showing a color change due to the conversion of PdO into Pd NPs upon H2 gas adsorption, with the color intensity measured using a detector and a LOD value of 1000 ppm for H2 gas. Ha et al.98 presented a wearable sweat pH sensor fabricated using curcumin and thermoplastic polyurethane for pH measurement via a color change reaction from enol to di-keto form. This sensor can be seamlessly affixed to a range of fabric materials through O2 plasma activation and thermal heating, making it a promising tool for continuous sweat pH monitoring, particularly beneficial for individuals with cystic fibrosis.
You and colleagues99 designed wearable multi-groove micro-needles for colorimetric monitoring of glucose levels in diabetic patients, employing microneedles prepared by photopolymerization of polyethylene glycol di-acrylate to penetrate the patient's skin, and extract internal fluid via a capillary process, with successful application demonstrated on mice for glucose monitoring. Zhang et al.100 demonstrated a flexible and stretchable colorimetric sensor for monitoring pH and ion concentrations. It features super hydrophilic assays made from thermoplastic polymer nanofiber textiles and silica NPs, combined with a superhydrophobic material for sweat focusing, with color changes efficiently measured using a smartphone.
Recent developments in portable colorimetric sensor technologies have brought positive impacts on sensing applications. Miniaturization and integration enable the development of small lightweight sensors that offer convenience for on-site and real-time analysis, eliminating the need for complex laboratory preparations.42,101 Wearable colorimetric sensors enable continuous monitoring and personalized healthcare, facilitating real-time identification of environmental and medical issues.102 He and his research group103 developed adaptable, skin-mounted colorimetric bands to monitor chloride, pH, calcium, and glucose levels in sweat samples. These bands use a superhydrophobic silica coating to channel sweat away from the skin into superhydrophilic micropatterns. The colorimetric changes are captured using a smartphone camera, allowing for precise quantitative analysis. This method offers a straightforward and user-friendly approach for health diagnostics in clinical settings. However, it is worth noting that these bands do not provide real-time monitoring and are affected by variations in the sweat rate. Xu et al.104 presented a novel technology, super-wettable microchips, for the colorimetric monitoring of glucose, calcium, and protein levels in the microgravity environment of the human body to track daily physiological variations. The team developed a superhydrophobic substrate and super-hydrophilic microwells, which serve as channels for collecting tiny sweat droplets. These collected samples were then subjected to specific reagents within the microchips, resulting in observable color changes. These color changes were documented using a camera to establish grayscale values for precise quantitative analysis. This compact device is user-friendly, lightweight, and doesn't require any electrical equipment for operation. Wu and colleagues105 carried out nucleic acid detection using a super-hydrophilic cotton thread. They initially loaded GNP/DNA conjugates onto a designated pad. Following the deposition of a sample containing the target DNA, a red-colored absorption band became visible to the naked eye after 15 min incubation. Quantitative analysis was performed by recording the optical density of the color band using a specialized instrument referred to as the “strip reader”, in combination with software provided by “GoldBio”.
Wearable colorimetry is a game changer in healthcare and environmental monitoring, allowing real-time tracking of parameters like glucose levels in sweat and skin surface pH changes. These sensors offer personalized and continuous health monitoring, enabling quick detection of medical issues and environmental factors. They also hold the potential for enhancing safety by monitoring gas concentrations in real time, promising a transformative impact on health and environmental monitoring.
Srivastava and Sharma76 developed a smartphone application-based portable spectrophotometer to stabilize and enable on-site monitoring of Fe3+ and Cu2+ ions in drinking water. The system's optimization included the use of standard buffer samples with known concentrations of Fe3+ and Cu2+ prior to the analysis of water samples, covering a concentration range of 0.001–5 ppm for heavy metals. Rajamanikandan et al.81 introduced a novel method to detect Cr3+ ions using a smartphone. The method covers a broad linear range (40–128 nM) and possesses a low LOD of 12.4 nM. Esfahani and group57 employed an AuNPs-MMA for portable colorimetric detection of phosphate ions in drinking water. By introducing Eu3+ ions, the AuNPs aggregate, changing their color from blue to red, enabling sensitive and selective phosphate detection with a low LOD of 0.3 μg L−1. Notably, the method demonstrated a commendable LOD value, estimated at 0.3 μg L−1. Budlayan and coworkers110 demonstrated a paper-based colorimetric sensor based on thiamine-functionalized AgNPs for the on-site detection of Hg2+. Herein, the sensor can detect Hg2+ with a noticeable detection range of up to 0.5 M when the color changes from yellowish to white. For samples of tap water and creek water spiked with Hg2+, the sensor's colorimetric response is constant and selective towards Hg2+. Rajamanikandan et al.111 demonstrated cysteine-functionalized AgNPs (Cys-AgNPs) for the smartphone-coupled paper-based colorimetric method for the analysis of toxic sulfide ions (S2−). Herein, in 2 min following the addition of S2− ions, the colour of Cys-AgNPs changed from yellow to colorless. The large linear range from 40 to 480 μM for determination of S2− ion was obtained with LOD value of 28 nM. In addition, various NMs such as Ag, Au, and Cu NPs and chromophoric dyes112–120 have been frequently used for the determination and on-site detection of environmental toxic metals and pollutants. Table 1 provides an overview of the environmental uses of portable colorimetric sensors for analyzing various chemical species in water samples.
Materials/probe | Substrate | Sensing method | Analyte | Linearity range | LOD | Samples | Ref. |
---|---|---|---|---|---|---|---|
Fuchsin dyes | Filter paper | Smartphone/RGB | NO2− | 0.005–9.2 mg L−1 | — | Water | 49 |
AuNPs-GSH | PET paper | Visual detection | Cd2+ | 10–100 nM | 18.8 nM | Potable water | 53 |
AuNPs-VPA | Filter paper | Smartphone/RGB | UO22+ | — | 2.0 μM | Water | 54 |
AuNPs-aptamer | Solution | Smartphone/RGB | Cd2+ | 2–20 μg L−1 | 1.12 μg L−1 | Water | 56 |
AuNPs-MACA | Solution | Visual detection/LSPR | PO42− | 0.3 μg L−1 | 10–26 μg L−1 | water | 57 |
AgNPs | Filter paper | Smartphone/RGB | Hg2+ | 40–1200 μg L−1 | 10 μg L−1 | Water | 60 |
AgNPs-PVA | Filter paper | Smartphone/RGB | Pb2+ | 50–1000 μg L−1 | 20 μg L−1 | Water | 61 |
AgNPs-AW | Filter paper | Smartphone/RGB | Hg2+ | 100 nM−100 μM | 28 nM | Water | 63 |
AgNPs-Acacia nilotica | Filter paper/solution | Smartphone/RGB | Hg2+ | 50–450 μM | — | Water | 65 |
AuNPs-MMT | Filter paper | Smartphone/RGB | Cr3+ | 40–128 nM | 12.4 nM | Water | 81 |
AuNPs/sucrose | Filter paper | Smartphone/RGB | As3+ | 50–3000 μg L−1 | 20 μg L−1 | Water and soil | 82 |
AgNPs-PVP | Filter paper | Smartphone/RGB | P2O74− | 0.2–2 μM | 0.2 μM | Water | 83 |
AgNPs | Filter paper | Smartphone/RGB | S2O32− | 0–20 μM | 1.0 μM | Water | 85 |
BG-triarylmethane dye | Filter paper | Visual detection | PO42− | 13.6–0.27 mg L−1 | 0.07 mg L−1 | Water | 87 |
AgNPs | Filter paper | Smartphone/RGB | Hg2+ | — | 0.86 μg L−1 | River water | 88 |
ZnFe2O4 MNPs | Cellulose paper | Visual detection | Bisphenol-A | 10–1000 nM | 6.18 nM | Water | 90 |
AgNPs | Filter paper | Visual detection | Cu2+ | 7.8–62.8 μM | 7.8 nM | Water | 91 |
AgNPs-thiamine | Filter paper | Portable/RGB | Hg2+ | — | 0.5 μM | Tap and river | 110 |
AgNPs-Cys | Filter paper | Smartphone/RGB | S2− | 0.4–4.8 μM | 28 nM | Tap and seawater | 111 |
AgNPs | Filter paper | Smartphone/RGB | Cl− | 10–1000 mg L−1 | 1.3 mg L−1 | Natural water | 112 |
AgNPs-carrageenan | Filter paper | Digital photometry/RGB | Hg2+ | 0.5–2.5 mM | 0.29 mM | Water | 113 |
AuNPs | Filter paper | Smartphone/RGB | Hg2+ | 0–2 μM | 50 nM | Drinking water | 114 |
AuNPs-Cyst | Filter paper | Smartphone/RGB | CN− | — | 159 nM | Drinking water | 115 |
AuNPs-hydrogel nanozyme | Filter paper | Smartphone/RGB | Hg2+ | 0.008–20 mg L−1 | 1.10 μg L−1 | River water | 116 |
AuNPs-maleic acid | Filter paper | Smartphone/RGB | Cr3+ | 0.2–2.0 μg L−1 | 0.1 μg L−1 | Lake water | 117 |
Nitrite + h p-sulfanilic acid | Solution | Smartphone/RGB | Triclosan | 3–200 μg L−1 | 0.8 μg L−1 | Water | 118 |
Molybdenum blue-PVA | Solution | Smartphone/RGB | NO2− | 0.1–1 mg L−1 | 0.02 mg L−1 | Drinking water | 119 |
Molybdenum blue-PVA | Solution | Smartphone/RGB | NO3− | 0.1–1 mg L−1 | 0.04 mg L−1 | Drinking water | 119 |
Molybdenum blue-PVA | Solution | Smartphone/RGB | PO42− | 0.25–5 mg L−1 | 0.14 mg L−1 | Drinking water | 119 |
Azophenol dye | Filter paper | Smartphone/RGB | Hg2+ | 0–10 μM | 8.1 nM | Water | 137 |
Hence, the development of portable smartphone-based spectrophotometers and the colorimetric detection method has greatly advanced environmental monitoring. These cost-effective innovations enable on-site quantification of trace levels of various substances, including chlorine, nitrite, Cu2+, Fe3+, and Cr3+. By using readily available materials and smartphone applications, they provide efficient, rapid, and reliable results comparable to traditional laboratory methods. These technologies hold promise for environmental scientists and field personnel in safeguarding public health and the environment, making them valuable tools for water analysis and environmental monitoring.
The body's regulation of sodium (Na+) is of most importance, necessitating regular monitoring. To address this need, Chandran and team68 developed an affordable paper strip to measure Na+ levels in blood and urine samples. The method involves immersing paper in yellow NPs, allowing it to dry, and introducing Na+ for visual color changes. It works for a broad Na+ range (20 to 250 mM) with a low LOD of 65 μM. Inamori and group77 reported an affordable wearable bilirubinometer for neonatal jaundice monitoring. This device also simultaneously measures the heart rate and oxygen saturation, providing comprehensive vital sign monitoring. Tested on 50 newborns undergoing phototherapy, it shows promise in aiding therapeutic decisions. Wang and colleagues36 presented an innovative self-healing adhesive hydrogel patch, which is assisted by a smartphone, for real-time colorimetric sweat detection. This patch, tailored for individual users, adheres securely to the skin, enabling the collection and analysis of sweat. Table 2 summarizes the applications of portable colorimetric sensing devices for the measurement of a variety of several chemical substances from clinical samples.
Materials/probe | Substrate | Sensing method | Analyte | Linearity range | LOD | Sample | Ref. |
---|---|---|---|---|---|---|---|
AuNPs-β-CD | Solution | Smartphone/RGB | Cysteine | 0.25–4.0 μM | 25.5 nM | Clinical sample | 58 |
CuNPs-curcumin | Filter paper | Smartphone/RGB | Na+ | 20–250 mM | 65 μM | Serum and urine | 68 |
CuNPs-MSA | Solution | Handheld colorimeter | Uric acid | 5 μM–4.5 mM | 3.7 μM | Urine | 69 |
CuNPs-MSA | Solution | Handheld colorimeter | H2O2 | 5–500 mM | 4.3 μM | Urine | 69 |
CuO-Maca | Filter paper | Smartphone/RGB | Dopamine | 0.625–5 μM | 16.9 nM | Clinical | 70 |
AuNPs | Transparency sheet | Smartphone/RGB | Vitamin B1 | 40–200 μg L−1 | 3.0 μg L−1 | Urine | 55 |
MoS2/PDA/CoCu | Solution | Smartphone/RGB | Uric acid | 0.5–200 μM | 0.13 μM | Serum and urine | 72 |
CuO@rGO | Filter paper | Smartphone/RGB | Glucose | 1–10 mM | 7.0–8.0 μM | Human blood | 121 |
AuNP@PVA@MO | Solution | Smartphone/RGB | H2O2 | — | 1.70 mM | Biological sample | 122 |
8-Hydroxy quinoline and sulfanilic acid | Solution | Smartphone/RGB | Atenolol | 8.0–60.0 mg L−1 | 2.13 mg L−1 | Pharmaceuticals | 125 |
The advent of portable colorimetric sensing has revolutionized point-of-care diagnostics, offering swift and cost-efficient analyses. Examples include smartphone-based Hb analyzers and multi-wavelength smartphone colorimetric readers, showcasing their accuracy and potential in healthcare. Additionally, innovations like paper strips for sodium monitoring, nonenzymatic dopamine sensing, wearable bilirubinometers, and self-healing adhesive hydrogel patches for sweat analysis demonstrate the versatility and promise of colorimetric technology in enhancing healthcare diagnostics and monitoring.
Fig. 12 Smartphone-based colorimetric determination of the nitrite ion in a meat sample [reprinted from ref. 40 with permission from American Chemical Society]. |
Silva and Rocha127 introduced a colorimetric sensing approach to determine adulterated protein in milk. Copper sulfate was added to the milk sample to precipitate protein, and then EDTA was added to react with the remaining copper sulfate, forming a blue-colored Cu–EDTA complex. The color of the complex was captured using a smartphone, and the RGB value was analyzed. The intensity of the blue-colored complex was inversely proportional to the level of adulterated protein in the milk. Lima and Coworkers128 presented a method to detect the presence of H2O2 as an adulterant in milk. This method involved adding iron(II) sulfate and potassium thiocyanate solution to the milk sample, leading to the oxidation of Fe2+ to Fe3+ in the presence of an oxidizing agent H2O2. The development of a red-colored iron(III) thiocyanate complex was quantified by analyzing the RGB values of a smartphone, thereby confirming the existence of H2O2 in the milk sample. Zhang et al.129 determined the presence of urea in milk using a smartphone-based portable colorimetric sensor. Prussian blue nanoparticles (PBNPs) and urease enzyme were added to the milk sample, resulting in the conversion of urea to CO2 and NH3 in the presence of urease, causing a change in the solution's pH. PBNPs are pH-sensitive NPs that change color with pH variation, and the smartphone captured the color change, allowing the calculation of the RGB value to assess the presence of urea in the milk sample. Liu et al.130 developed a smartphone-based portable colorimetric sensor for NO2− sensing in food, based on a hydrogel microsphere substrate. Herein, N-(1-naphthyl) ethylenediamine was mixed with sodium alginate and further a microsphere was formed bteween Ca2+ and sodium alginate due to the strong chelation process. This microsphere shows high sensing properties of NO2− ions. Pickles and sausages just needed to be simply homogenized before measurements, whilst water and milk samples could be measured directly without any prior preparation. Gao and colleague131 developed a paper-based colorimetric sensor based on citrate-capped AuNPs for the melamine determination in milk samples. Herein, citrate-capped AuNPs were stabilized using Triton X-100, protecting them from high ionic strength and pH range. However, melamine produced aggregation and destabilization, which resulted in a color shift from red wine to blue. A paper-based colorimetric quantitative detection system was coupled with a smartphone. This colorimetric sensor to successfully identify melamine in a milk sample in the 0.75–1.75 μM linear range and with 5.1 nM LOD value. Chaisiwamongkhol et al.132 designed a smartphone-coupled paper-based colorimetric sensor for the determination of sibutramine adulterants in food supplements. Herein, citrate-capped AuNPs have been used as a sensing probe for sibutramine analysis. The approach has a LOD and LOQ of 1.15 M and 3.47 M, respectively, with an accuracy of 92–107%. The technique can be used to detect and measure chemicals that have been misused instead of highly technical instruments. Sangsin and coworkers133 developed a smartphone-assisted paper-based colorimetric sensor for the detection of Cr3+ in food samples. Herein AgNPs were used as a functionalized material and deposited on a paper substrate for on-site monitoring of Cr3+. A smartphone readout system was used to create a low-cost portable way to detect Cr3+. In a short period of time, the system monitors color intensities in the AgNP system. The system is very selective with a linear range of 2.0–5.0 mg L−1, and 1.52 mg L−1 of LOD; it has been successfully employed for dietary supplement quantification, demonstrating practicality and reproducibility for on-site Cr3+ detection in real samples. A paper-based food safety process using different sensing probes such as NMs and dyes134–137 ensures quality checks, tracks contamination, and educates users, enhancing the overall food safety through accessible, cost-effective, and efficient methods. Table 3 summarizes the applications of portable colorimetric sensing devices for the measurement of a variety of several chemical substances from food samples.
Materials/probe | Substrate | Sensing method | Analyte | Linearity range | LOD | Sample | Ref. |
---|---|---|---|---|---|---|---|
4′-Hydroxyl-2,4-diaminoazobenzene | Paper | Smartphone/RGB | Al3+ | 20 μM −2.0 mM | 2.36 μM | Food and toothpaste | 47 |
4′-Hydroxyl-2,4-diaminoazobenzene | Paper | Smartphone/RGB | Fe3+ | 20 μM–2.0 mM | 2.68 μM | Food and toothpaste | 47 |
CuONPs-Camellia sinensis polyphenols | Filter paper | Smartphone/RGB | NH3 | 12.5–100 μM | 40.6 nM | Food supplements | 71 |
Cu@Ag NPs | Filter paper | Smartphone/RGB | Dimethoate | 100–2000 μg L−1 | 30 μg L−1 | Food | 73 |
Fe-SAN | Solution | Smartphone/RGB | Ascorbic acid | 0.5–100 μM | 0.315 μM | Tropical fruits | 86 |
1,2-Naphthoquinone-4-sulfonate | Wax printed paper | Computer/RGB | Phenacetin | 0–64.52 mg L−1 | 3.5 mg L−1 | Seized cocaine sample | 92 |
AgNPs-carrageenan | Filter paper | Digital photometry | Hg2+ | — | 292 μM | Environmental sample | 113 |
Polymer | Filter paper | Smartphone/RGB | NO2− | 1–300 | 0.85 mg L−1 | Meat | 126 |
Prussian blue NPs | Filter paper | Smartphone/RGB | Urea | 0.5–5 mM | 0.27 mM | Milk | 129 |
AuNPs-Triton X100 | Filter paper | Smartphone/RGB | Melamine | 0.75–1.75 μM | 5.1 nM | Milk | 131 |
AuNPs | Filter paper | Smartphone/RGB | Sibutramine | 5–15 μM | 3.47 μM | Food supplements | 132 |
AgNPs | Filter paper | Smartphone/RGB | Cr+3 | 2–5 mg L−1 | 1.52 mg L−1 | Dietary supplement | 133 |
AgNPs-Lepidium meyenii polyphenols | Filter paper | Smartphone/RGB | H2O2 | 0.5–5000 μM | 3.84 μM | Milk | 134 |
AgNPs | Filter paper | Smartphone/RGB | H2O2 | 0.1–10 mM | 0.1 mM | Food supplement | 135 |
AgNPs-metronidazole | Filter paper | Smartphone/RGB | Permethrin | — | 0.010 μM | Tomato and apple | 136 |
AgNPs-green dendrimer-coated matcha extract | Filter paper | Smartphone/RGB | H2O2 | 0.05–20 μM | 0.82 μM | Food supplement | 137 |
Therefore, portable colorimetric sensing is vital for ensuring food safety by enabling real-time detection of pollutants, allergens, and spoilage indicators. Utilizing nanomaterials and chromophoric reagents assisted with smartphone-based systems, it empowers food professionals to swiftly identify risks, maintain safety standards, and educate consumers. A range of smartphone-assisted colorimetric devices have been developed for detecting various food contaminants, offering accessible, cost-effective, and efficient methods to enhance food safety and public health.
The surprising innovation in nanomaterials and chromophoric dyes has improved the sensitivity and selectivity of portable colorimetric sensors. The use of label-free and signal amplification methods, which have enhanced detection limits and increased analyte selectivity, has been made possible by the use of nanomaterials such as nanoparticles, quantum dots, and nanostructured materials. In addition, the development of mobile sensing devices like smartphones and paper-based systems has opened up access to analytical data. On-the-go and point-of-care diagnostics are now possible because of the accessibility and affordability of cell phones, especially in resource-constrained areas where access to conventional laboratory facilities is constrained. Paper-based detecting systems offer an ecologically safe and cost-effective substitute for rapid detection, especially in remote areas or during emergencies.
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