Next Article in Journal
Urgent Need for Field Surveys of Coronaviruses in Southeast Asia to Understand the SARS-CoV-2 Phylogeny and Risk Assessment for Future Outbreaks
Next Article in Special Issue
Synthetic Biology towards Improved Flavonoid Pharmacokinetics
Previous Article in Journal
Advanced Killing Potential of Thymol against a Time and Temperature Optimized Attached Listeria monocytogenes Population in Lettuce Broth
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Review

Construction of DNA Biosensors for Mercury (II) Ion Detection Based on Enzyme-Driven Signal Amplification Strategy

School of Life Sciences, East China Normal University, Shanghai 200241, China
Submission received: 10 February 2021 / Revised: 4 March 2021 / Accepted: 5 March 2021 / Published: 8 March 2021

Abstract

:
Mercury ion (Hg2+) is a well-known toxic heavy metal ion. It is harmful for human health even at low concentrations in the environment. Therefore, it is very important to measure the level of Hg2+. Many methods, reviewed in several papers, have been established on DNA biosensors for detecting Hg2+. However, few reviews on the strategy of enzyme-driven signal amplification have been reported. In this paper, we reviewed this topic by dividing the enzymes into nucleases and DNAzymes according to their chemical nature. Initially, we introduce the nucleases including Exo III, Exo I, Nickase, DSN, and DNase I. In this section, the Exo III-driven signal amplification strategy was described in detail. Because Hg2+ can help ssDNA fold into dsDNA by T-Hg-T, and the substrate of Exo III is dsDNA, Exo III can be used to design Hg2+ biosensor very flexibly. Then, the DNAzyme-assisted signal amplification strategies were reviewed in three categories, including UO22+-specific DNAzymes, Cu2+-specific DNAzymes and Mg2+-specific DNAzymes. In this section, the Mg2+-specific DNAzyme was introduced in detail, because this DNAzyme has highly catalytic activity, and Mg2+ is very common ion which is not harmful to the environment. Finally, the challenges and future perspectives were discussed.

1. Introduction

Mercury ion (Hg2+) is a well-known toxic heavy metal ion. It comes from both natural sources (such as oceanic emissions and volcanic eruptions) [1,2] and anthropogenic sources (such as the mining industry, combustion of fossil fuels and solid waste) [3,4,5]. Since Hg2+ has high affinity to thiol groups to form Hg-S chemical bonds, it can cause the inactivation of some enzymes and proteins thus leading to some illnesses such as loss of hearing, speech, vision or motor and cognitive disorders [6,7,8]. Meanwhile, Hg2+ can also accumulate in human body through the food chain, so it is harmful for human health even at low concentrations in the environment [9]. Additionally, Hg2+ can be converted to methyl mercury under the action of organisms such as living bacteria [8]. Methyl mercury is a very toxic neurotoxin which can cause permanent brain damage brain. The World Health Organization (WHO) and the USA Environmental Protection Agency (EPA) have regulated the maximum contaminant level for Hg2+ to be below 10 nM in drinking water. Therefore, it is very important to measure the level of Hg2+.
So far, there have been many methods to detect Hg2+ based on instruments (such as atomic absorption spectroscopy) [10,11,12], small organic molecules [13,14,15], proteins [16], DNA [17,18,19] and so on. Among these methods, DNA (oligonucleotide) biosensors have attracted much attention because DNA is stable, cheap, and easy to obtain as well as to modify. In 2004, Ono and Togashi first discovered that Hg2+ could specifically bind to thymine (T) to form the T-Hg-T mismatch [20]. Then, they designed the first DNA biosensor to detect Hg2+ by modifying quencher and fluorophore at the two ends of the thymine-rich DNA. In fact, the binding constant of T-Hg-T is higher than Watson-Crick pair (T-A), so a T-Hg-T mismatch can easily replace a T-A pair [21,22]. According to this phenomenon, Lu group developed a new biosensor for detecting Hg2+ in 2008 [23]. Since then, many DNA biosensors have been designed and developed based on T-Hg-T mismatch [24,25,26]. Since the maximum residue limits (MRL) of Hg2+ is as low as only 10 nM, many signal amplification strategies have also been developed concomitantly to improve the sensitivity of the Hg2+ DNA biosensors [27,28,29,30,31], such as those based on nanomaterials [30,32] and enzyme-driven signal amplification. Subsequently, because many enzymes are commercial and the quality between batches can be easily controlled, the enzyme-driven signal amplification has become a convenient approach for mercury sensing. Until now, several reviews have been published on DNA biosensors for the detection of Hg2+ [33,34,35]. However, few reviews on the strategy of enzyme-driven signal amplification have been reported. In this paper, we reviewed this topic by dividing the enzymes into nucleases and DNAzymes according to their chemical nature. For nucleases, exonuclease III (Exo III), exonuclease I (Exo I), nicking endonuclease (Nickase), duplex-specific nuclease (DSN) and deoxyribonuclease I (DNase I) were used as representatives to illustrate. For DNAzymes, they were divided into three categories, UO22+-specific DNAzymes, Cu2+-specific DNAzymes and Mg2+-specific DNAzymes. This review will help readers better understand the application of enzyme-driven signal amplification strategy in the construction of Hg2+ DNA biosensors.

2. Nucleases

Nucleases are a class of enzymes that cleave nucleic acids. Their chemical nature is proteinic. They usually have the structures or sequences which are specific for the substrate therefore are often used as tool enzymes for genetic engineering. With the development of life science, many different kinds of nucleases have been discovered with different functions (Figure 1, Table 1). Generally, they include restriction endonuclease, duplex specific nuclease, exonuclease, nicking endonuclease, RNase, and so on. In DNA biosensors, we can control the formation or disappearance of the nucleases action site by adding target in the designing of the biosensor. In this process, the enzymes are not consumed. Therefore, they can be used for the signal amplification [36,37,38]. Here, we chose five common nucleases (exonuclease III, exonuclease I, nicking endonuclease, duplex-specific nuclease and deoxyribonuclease I) as representatives to illustrate their applications of enzyme-driven signal amplification strategy in Hg2+ DNA biosensors.

2.1. Exonuclease III

Exonuclease III (Exo III) is a member of the exonuclease family. It can remove the mononucleotides from 3′-end of double-stranded DNA. Typically, it is a double-stranded specific nuclease. The 3′-end overhangs over four bases of double-stranded DNA or single-stranded DNA can prevent the degradation by Exo III. Since Hg2+ can promote the single-stranded rich thymine DNA to form double-stranded structure via T-Hg-T mismatch, Exo III can be used to design DNA biosensors by digesting this double-stranded structure to induce a chain of reactions [39,40,41,42].

2.1.1. Exo III-One Cycle

In 2019, Ma; et al. reported a fluorescence DNA biosensor to detect Hg2+ based on Exo III-assisted signal amplification together with silver nanoclusters [43]. This DNA biosensor was a T-rich DNA with silver nanoclusters (DNA-AgNCs). It could bind to positively charged gold nanoparticles (AuNPs) through negatively charged phosphoric acid skeleton. Then, the fluorescence of DNA-AgNCs could be quenched by AuNPs, therefore there was no fluorescence signal in the initial state. In the presence of Hg2+, DNA-AgNCs could form a DNA duplex via T-Hg-T mismatch. This structure could be digested into small DNA fragments by Exo III. As a result, the AgNCs were separated from AuNPs and the fluorescence signal was recovered. Meanwhile, Hg2+ was also released and could be used in the next cycle (Figure 2a). Therefore, a small amount of Hg2+ could cause a huge accumulated increase in fluorescence. Accordingly, the sensitivity of the method was improved with a detection limit as low as 2.3 pM.
In 2018, Ding; et al. developed a label-free fluorescence DNA biosensor for detecting Hg2+ based on Exo III-aided signal amplification and G-quadruplex DNA [26]. In this DNA biosensor, three DNA probes (P1, P2, P3) were involved. The 3′-end of P1 and 5′-end of P2 contained poly-T sequences. Meanwhile, the 5′-end of P3 contained a G-quadruplex sequence. In the absence of Hg2+, P1, P2, P3 were all in free single stranded DNA state. Thus, they could not be recognized and cut by Exo III. At this status, the G-quadruplex sequence could form a cage-like structure which could bind N-methylmesoporphyrin IX (NMM) to emit fluorescence signal [44,45]. In the presence of Hg2+, P1 and P2 could form a T-shaped platform with the help of T-Hg-T mismatch. Then, P3 could bind to this T-shaped platform by base complementation to form a partial double chain structure which could be digested by Exo III. As P1 was degraded, the G-quadruplex sequence was cut and the cage-like structure could not be retained to trap NMM. As a result, the fluorescence signal decreased. Meanwhile, the T-shaped platform was released and entered the next cycle to cause more destruction of G-quadruplex (Figure 2b). At last, the highly sensitive DNA biosensor was realized with a detection limit as low as 1.0 pM.
In 2017, Hong et al. reported a colorimetric DNA biosensor for the detection of Hg2+ using Exo III-assisted signal amplification and AuNPs [46]. In this DNA biosensor, a hairpin-shaped DNA probe (H-DNA) with G-quadruplex sequence was designed. In particular, it was rich in T bases at both ends. In the absence of Hg2+, the H-DNA could bind with AuNPs and protect them from aggregation in solutions of high ionic strength. In this status, the separate AuNPs showed red color. In the presence of Hg2+, the terminal of the H-DNA could form a DNA duplex stem via T-Hg-T mismatch. Then, Exo III could digest this structure from the 3′-terminal of the H-DNA. The digestion of H-DNA led to the release of Hg2+ and the 5′-terminal of the H-DNA. The free Hg2+ kept on binding the next H-DNA to cause more DNA to be cut. In the presence of K+, the free 5′-terminal of the H-DNA could form the G-quadruplex structure which lost the ability to protect AuNPs. Thus, the aggregated AuNPs led to a color change from red to blue in the high ionic solutions. The color change could be easily observed by the naked eye (Figure 2c). With the Exo III-assisted signal amplification strategy, the ultrasensitive colorimetric DNA biosensor was obtained with the detection limit as low as 3.2 pM.
In addition to fluorescence and color methods, electrochemical methods have also been used to detect Hg2+. In 2018, Fu; et al. reported a homogeneous electrochemical DNA biosensor for Hg2+ determination based on the Exo III-assisted recycling amplification and indium tin oxide (ITO) electrode [47]. In this DNA biosensor, methylene blue (MB) was modified at the 3′-end of the DNA probe to form MB-TDNA. The poly T sequence was also introduced at the 3′-end of MB-TDNA. The partially complementary DNA (cDNA) of MB-TDNA with poly T sequence in its 5′-end was used (Figure 2d). In the absence of Hg2+, the 5′-end of MB-TDNA and 3′-end of cDNA could form a corresponding duplex. Subsequently, the cDNA was cut by Exo III, however, MB-TDNA kept intact. Because the phosphate backbone of MB-TDNA had a large negative charge which was repulsed from the negatively charged ITO electrode, the electrochemical signal was low. When Hg2+ was added, it helped cDNA and MB-TDNA form a complete double chain structure via T-Hg-T mismatch. This structure could be digested by Exo III. As a result, MB and Hg2+ dissociated from the DNA probe. Then free MB moved close to the surface of ITO electrode to produce a significant current signal. Meanwhile, free Hg2+ induced a new hybridization and produced more free MB. This homogeneous electrochemical DNA biosensor had a linear range of 1.0 nM–0.5 μM with a detection limit of 0.38 nM.

2.1.2. Exo III-Multiple Cycles

Except for the single-loop amplification strategy, Exo III can also induce multiple cycle signal amplification to achieve higher sensitivity [48,49]. In 2019, Song et al. developed a colorimetric DNA biosensor for the visual detection of Hg2+ based on Exo III-driven double-cycle signal amplification strategy and AuNPs [50]. At the beginning, DNA-C and its partial complementary chain DNA-L* formed a duplex structure. When Hg2+ was added, it helped DNA-C* to replace DNA-L* by forming stronger T-Hg-T mismatch. The DNA-C on the DNA-C-C* duplex structure could be degraded by Exo III. Then DNA-C* was released to replace another DNA-L* from DNA-C-L*. In this cycle, a lot of free DNA-L* could be obtained. Subsequently, free DNA-L* entered cycle II which was also induced by Exo III. In cycle II, AuNPs modified with DNA-L (AuNPs-L) were hired to produce color signal. Free DNA-L* could bind with its complementary chain DNA-L to form AuNPs-L-L* duplex structure. This structure could also be cut by Exo III. After the AuNPs-L-L* duplex was degraded, DNA-L* was released again and induced more DNA-L to be degraded. As a result, AuNPs-L became AuNPs. Finally, the AuNPs without DNA protection could aggregate in a high-salt solution, which produced a color change from red to violet (Figure 3a). With two rounds of the signal amplification (cycle I and II), the colorimetric and visual Hg2+ biosensor was realized with a detection limit as low as 0.9 nM and an extra wide detection range of 1 nM to 10 μM.
In 2018, Song et al. reported a ultrasensitive electrochemical for the detection Hg2+ based on Exo III-assisted double-cycle signal amplification strategy and gold electrodes (AuE) [51]. In this DNA biosensor, a label-free hairpin probe (HP1) was designed which had a protruding 3′-terminal. The 3′-terminal contained a lot of T bases for targeting Hg2+. Another hairpin probe (HP2) was modified on the surface of the AuE by its 5′-terminal. The 3′-terminal of HP2 was labeled by methylene blue (MB). In the absence of Hg2+, the hairpin structure of HP2 was not open. MB and AuE were close enough to induce a large electrical signal. In the presence of Hg2+, the primer DNA could bind HP1 to form the duplex structure via T-Hg-T mismatch. This structure could then be digested from the 3′-terminal of HP1. As a result, the 5′-terminal of HP1 (Helper), primer DNA and Hg2+ were all released. The primer DNA and Hg2+ could bind another HP1 to form another new Helper. Thus, more Helper could be obtained in cycle I. In cycle II, Helper could bind HP2 to open the hairpin structure by forming another duplex structure (Helper-HP2). The Helper-HP2 duplex could be recognized by Exo III. Along with the procedure that Exo III digested Helper-HP2 from the 3′-terminal of HP2, MB and Helper were released. Free Helper could bind another HP2 to release more free MB (Figure 3b). As a result, free MB was farther from AuE, thus the electrical signal had a distinct decrease. The detection limit of this ultrasensitive electrochemical biosensor was 227 pM.
In 2020, Zhou et al. designed a fluorescence DNA biosensor for the Hg2+ detection using a similar signal amplification strategy and G-quadruplex/NMM as a reporter [52]. In this DNA biosensor, two hairpins DNA (hairpin A and hairpin B) were designed with 3′-protruding terminals which could resist the Exo III digestion. In the presence of Hg2+, Hg2+ could help DNA1 hybridize with the 3′-terminal of hairpin A via T-Hg-T mismatch. The DNA1- hairpin A could be cut by Exo III form the 3′-terminal of hairpin A. Then, DNA1, Hg2+ and the 5′-terminal of hairpin A (e-d-c) were released. Afterwards, DNA1, Hg2+ could activate another round of the cleavage reaction to produce more e-d-c. Likewise, the e-d-c hybridized with the 3′-terminal of Hairpin B via T-Hg-T mismatch. Under the Exo III digestion, the 5′-terminal of hairpin B was obtained which was also DNA e-d-c. DNA e-d-c was released and reused to trigger the next round digestion (Figure 3c). At last, large amounts of DNA e-d-c were obtained through two rounds of signal amplification (cycle I and II). Then, DNA e-d-c with G-rich sequence could form G-quadruplex structure in the presence of K+. Finally, G-quadruplex structure could bind with NMM to emit intense fluorescence. The autocatalytic DNA biosensor was very sensitivity with the detection limit of 10 fM.
The Exo III-assisted signal amplification strategy can also be used in combination with other amplification methods [53]. In 2021, He et al. reported a triple signal amplification strategy for ultrasensitive Hg2+ detection based on a DNA dual cycles, organic-inorganic hybrid nanoflowers (Cu3(PO4)2HNFs) and AuNP probe (Figure 3d) [54]. In the first strategy, hairpins DNA (HP1) containing report DNA (RDNA) was designed. In the presence of Hg2+, it caused the two ends of HP1 to form double-stranded structures via T-Hg-T mismatch. The cycle was triggered by Exo III to digest the 3′-end of HP1. After the digestion, Hg2+ was released for the next cycle and large amounts of RDNA were obtained. The free RDNA could form a new double stranded DNA with another hairpin DNA (HP2) which had been modified on the electrode (Au/GCE). Subsequently, the third hairpin DNA (HP3) was used to open the new dsDNA. The RDNA was released again for the next cycle. At a result, HP3 was connected on the electrode by the DNA dual cycles amplification. In the second strategy, the (Cu3(PO4)2HNFs)@AuNPs@c-probe was synthesized. This complex was effectively anchored on the Au/GCE by complementary base between c-probe and HP3. Due to the nanoflowers with a high surface area, it could carry lots of signal molecules to amplify signal. In this paper, signal molecule R-probe@AuNPs was synthesized by modifying r-probe 1 and r-probe 2 marked with ferrocene on the AuNPs. Then, the R-probe@AuNPs was linked into the nanoflowers by c-probe. Since the AuNPs also had high surface area, it could carry many ferrocene molecules. Thus, the AuNPs acted as the third amplification strategy. Finally, this ultrasensitive electrochemical biosensor had an ultra-low detection limit of 0.19 fM by the triple signal amplification strategy.

2.2. Exonuclease I

Exonuclease I (Exo I) is another member of the exonuclease family. It is different from Exo III and its substrate is single-stranded DNA. The cutting directions of them are consistent, both from the 3’-end to the 5’-end. Hg2+ is commonly used to help form double-strands via T-Hg-T mismatch. And the double-strands cannot be digested by Exo I. However, the remaining single-stranded DNA without binding to Hg2+ can be cut. Thus, Exo I can also be used to design Hg2+ DNA biosensor. Since Hg2+ cannot be released repeatedly, this method is rarely used. Here, we give two examples to illustrate this method.
Yuan et al. reported a label-free fluorescence biosensor for the detection of Hg2+ based on Exo I [55]. In the absence of Hg2+, the single-stranded T-rich DNA (ssDNA) could be digested by Exo I. When the DNA dye was added, no signal was observed. In the presence of Hg2+, the ssDNA were folded into hairpin-like double-stranded DNAs (dsDNA). This dsDNA could not be digested by Exo I (Figure 4a). Thus, the DNA protected by Hg2+ could still bind with DNA dye to emit fluorescence signal. This DNA biosensor had a high sensitivity for Hg2+ detection with the detection limit of 15 nM.
To improve the sensitivity, some simple devices can be used in combination with Exo I. For example, Li; et al. developed an optical ultrasensitive DNA biosensor to detect Hg2+ by using dark-field microscope and Exo I [56]. In this biosensor, the complementary strand of Hg2+ aptamer was modified on the AuNPs. In the absence of Hg2+, the complementary strand and aptamer hybridized into a double-stranded structure (dsDNA) which could not be cut by Exo I. The dsDNA could prevent AuNPs from aggregation in the solution of NaCl. In the presence of Hg2+, the aptamer dissociated from the AuNPs and subsequently formed stronger interactions with T-Hg-T. Then, the single complementary strand was digested by Exo I to cause the release of AuNPs. In the solution of NaCl, the AuNPs aggregated with the color change (Figure 4b). The intensity of color change could then be observed and calculated by dark-field microscope. Because the sensitivity of the microscope was much higher than that of the naked eye, the ultrasensitive DNA biosensor was realized with the limit of detection as low as 36 fM and a linear range from 83 fM to 8.3 μM.

2.3. Nicking Endonuclease

Nicking endonucleases (nickases) are members of the endonuclease family. They can specifically recognize the restriction sites in the double-chain state and cut single-stranded DNA at that site. Because they only cut one strand of DNA, the other strand of DNA can be retained for signal amplification. This nickase-assisted amplification strategy has been developed for the detection of different targets including Hg2+ [57,58,59,60]. Depending on their recognition sequence, there are many different types of nickase such as Nt.AlWI [61], Nt.BstNBI [62], Nb.BbvC [63] and so on. The abundance of these nickases provides convenience for the design of DNA biosensor.
For example, back to 2011, Nt.AlWI was used to detect mercury ions by Li et al. [64]. In this biosensor, ferrocene (Fc)-ssDNA was modified on the Au electrode. In the presence of Hg2+, the Fc-ssDNA switched into a hairpin structure via T-Hg-T mismatch. The hairpin structure contained a cleavage site of Nt.AlWI. Along with the digestion of Nt.AlwI, Fc was released to increase the distance from the electrode. Thus, the electrical signal gradually decreased as the mercury ions increased. Since this method did not use cyclic amplification, the limit of detection was at the micromole level. Subsequently, Ma et al. reported a signal amplification biosensor that also used Nt.AlwI [65]. In this DNA biosensor, the streptavidin-coated quantum dots (QDs) was used to conjugate biotinylated hairpin-shaped probe A with a quencher. The probe A had a cleavage site of Nt.AlwI in the loop region. Due to the single state, it could not be cut by Nt.AlwI. At the beginning, the fluorescence of the QDs was quenched by quencher due to the short distance. In the presence of Hg2+, another DNA probe B hybridized with probe A to form a duplex structure via T-Hg-T mismatch. Probe A in the duplex structure could be digested to increase the distance between the quencher and the QDs. Thus, the fluorescence of the QDs was recovered. Meanwhile, the intact probe B and Hg2+ entered a new cycle to digest more probe A (Figure 5a). After the cyclic amplification, a remarkable signal was achieved. With the help of Nt.AlwI, the sensitivity of this biosensor was increased with the detection limit of 0.8 nM.
In recent years, nickase-assisted amplification strategy has also been reported for more DNA biosensor to detection of Hg2+. In 2019, Vijayan et al. developed a highly sensitive biosensor for Hg2+ detection based on luminescence resonance energy transfer (LRET) between nanoparticles and SYBR Green I [66]. In this biosensor, the upconversion nanoparticles NaYF4: Yb3+/Tm3+ (UCNPs) were synthesized and modified by hairpin DNA (DAN-1) containing thymine bases. At the beginning, DAN-1 could form a hairpin structure to bind SYBR Green I. Under the excitation at 980 nm, the UCNPs had strong visible bands at 477, 650 and 800 nm. And the absorption of the SYBR Green I was exactly 477 nm. Thus, the emission intensity of 477 nm decreased. In the presence of Hg2+, DAN-1 bound with DNA- mismatch to form a completely complementary dsDNA via T-Hg-T mismatch. This structure could be recognized by nicking enzyme. Then, DAN-1 was digested; the DNA- mismatch and Hg2+ were released to trigger a new cycle (Figure 5b). Since DNA-1 was degraded, SYBR Green I was also free. Therefore, the 477 nm emission of UCNPs was recovered. With the help of nickase-assisted amplification strategy, the sensitivity of this biosensor was as low as 0.14 nM.
In 2019, Liu et al. designed an Hg2+ DNA biosensor based on nickase-assisted signal amplification and DNA assembly [68]. In this biosensor, another nickase, Nt.BstNBI, was employed. Besides, four DNA probes were designed. They were a recognition probe (L), semi-enzyme-A (P1), semi-enzyme-B (P2) and fluorescein/quencher labeled reporting probes (PL), respectively. Without Hg2+, the four probes were all free. No fluorescence signal was observed, because of the intact quenching system. When Hg2+ was added, L, P1 and P2 could bind together to form an I-shaped DNA assembly structure via T-Hg-T mismatch (Figure 5c). Then PL could hybridize with this I-shaped structure by base pairing. Then, the cleavage sites of Nt.BstNBI appeared in the stem of the I-shaped junction. With Nt.BstNBI added, PL was cut to separate fluorescein from the quencher. Thus, the fluorescence signal could be recorded. Meanwhile, the I-shaped structure was also released to hybridize with another PL. At last, a lot of PL was cleaved to emit strong fluorescent signal in the presence of a small amount of Hg2+. The detection limit of this simple biosensor was 1.7 nM.
In addition, nickase can also be used in combination with other enzymes to improve the sensitivity of DNA biosensor. In 2016, the Yuan group developed a sensitive electrochemical biosensor to detect Hg2+ based on nickase Nt.BbvCI and terminal deoxynucleotidyl transferase (TdT) [67]. In this biosensor, two hairpins DNA (HP1 and HP2) were designed. HP1 was a T-rich DNA. Without Hg2+, its 5′-end was covered by forming hairpin structure. In the presence of Hg2+, the 5′-end exposed to form output DNA by conformation changes via T-Hg-T mismatch. HP2 was modified on the Au/GCE electrode by its 5′-end. The 3′-end was labeled by PO4 to block the TdT reaction. The output DNA could hybridize with HP2 to open the hairpin structure and form the output DNA-HP2 complex. This complex could be recognized by Nt. BbvCI and the 3′-PO4 of HP2 was cut off. Meanwhile, the output DNA was released to hybridize with another HP2 (Figure 5d). Accompanying with the cleaving of HP2, the substantial 3′-OH group exposed. Then, 3′-OH of HP2 could be added with a lot of deoxyadenosine triphosphate (dATP) to form a long ssDNA nanotail with the help of TdT and dATP. The ssDNA nanotail with negatively charged DNA skeleton could absorb the positively charged silver ions. In the presence of reduction regent sodium borohydride, the silver ions transformed into silver nanoparticles. The nanoparticles could deposit on electrode surface to output electrochemical signal. With the help of two enzymes, the sensitivity of this biosensor was improved with an ultralow detection limit of 3 pM.

2.4. Duplex-Specific Nuclease

Duplex-specific nuclease (DSN) is another member of the endonuclease family. It can selectively cleave dsDNA or the DNA in DNA-RNA hybrid duplexes. However, it cannot cut the ssDNA. Since Hg2+ can help ssDNA fold into dsDNA which can be digested by DSN to release Hg2+, DSN can also be used to amplify signal. In 2017, Xia group designed a highly sensitive fluorescence biosensor to test Hg2+ based on DSN and aggregation-induced emission (AIE) [69]. In this biosensor, fluorogen TPE was modified on the ssDNA to form a simple AIEgens functional nucleic acids (AFNAs) probe. In the absence of Hg2+, AFNAs probe exhibited a weak fluorescence signal. In the presence of Hg2+, the AFNAs probe changed the conformation from ssDNA to dsDNA via T-Hg-T mismatch. Then, the dsDNA was digested by DSN to released Hg2+ and fluorogen TPE. Hg2+ could be reused to bind new AFNAs probe. The fluorogen TPE could form supramolecular aggregate to enhance the fluorescence signal by AIE phenomenon (Figure 6). The sensitivity of this DNA biosensor was improved because Hg2+ was reused with the help of DSN. The detection limit of this simple DNA biosensor was 10 fM with a good linearity range from 10 fM to 1 nM.

2.5. Deoxyribonuclease I

Deoxyribonuclease I (DNase I) is DNA specific endonuclease which can degrade dsDNA and ssDNA. Mechanically, ssDNA can be absorb on the nanomaterial, while Hg2+ can shed DNA from the nanomaterial by promoting ssDNA to dsDNA via T-Hg-T mismatch. Then, free dsDNA can be digested by DNase I to release Hg2+. Thus, DNase I also can be used to amplify signal.
Wei et al. designed a nano-graphite-DNA hybrid fluorescent biosensor for Hg2+ detection based on DNase I for the first time [70]. In this biosensor, a T-rich ssDNA was labeled by fluorophore FAM. Without Hg2+, ssDNA was absorbed on the nano-graphite by π-π stacking [71,72] and the fluorescence of FAM was quenched by nano-graphite. Thus, no fluorescence signal was obtained. In the presence of Hg2+, ssDNA folded into dsDNA via T-Hg-T mismatch to detach from the nano-graphite surface. Free ssDNA could be cleaved by DNase I to release Hg2+ and FAM. The fluorescence of FAM was recovered. Hg2+ was reused in next cycle to lead to the signal amplification (Figure 7a). This amplified biosensor was simple and cost-effective with a detection limit of 0.5 nM.
Recently, Lu et al. reported a novel electrochemical biosensor to monitor Hg2+ based on DNase I-assisted target recycling [73]. In this biosensor, a methylene blue (MB)-labeled poly-T(15) oligonucleotide probe was designed to generate electrochemical signal. At the beginning, the probe was attached on the graphene oxide nanosheets/Au electrode by π-π stacking [74]. Since the graphene oxide nanosheets could protect MB-poly-T(15) from DNase I cleavage. The electrochemical signal was high. When Hg2+ was added, the MB-poly-T(15) ssDNA folded into dsDNA via T-Hg-T mismatch. And dsDNA was released from the electrode. Then, it was cut by DNase I to release free Hg2+ and MB. Free Hg2+ entered the next cycle to release numerous MB (Figure 7b). Due to the distance increasing between MB and the electrode, the electrical signal decreased. By the DNase I-triggered target recycling reaction, the biosensor had a high sensitivity with a detection limit of 0.12 nM.

3. DNAzyme

DNAzyme is a kind of DNA with catalytic activity. Its chemical nature is deoxyribonucleotides which is different from nuclease. The ribozyme (RNAzyme or DNAzyme) was discovered earlier than protease. The first RNAzyme was the ribosomal RNA intervening sequence of Tetrahymena which was discovered in 1982 [75], the first DNAzyme named GR5 was isolated by Breaker and Joyce in 1994 [76]. These discoveries changed the notion of enzyme that all enzymes were proteins. Many DNAzymes require metal ions as cofactors to attack phosphorus atoms in the substrate phosphoric acid skeleton, and many DNAzymes were screened in vitro [77,78,79]. Thus, the DNAzymes can at least be used to design a biosensor to detect their cofactors. Because Hg2+ has a weak interaction with phosphate, and high concentration of Hg2+ can cause the denaturation of DNA, it is difficult to obtain Hg2+-specific DNAzyme [80]. The Hg2+-specific DNAzyme named 10–13 was selected using amino/imidazole modified library by Perrin group, and then this group designed a DNAzyme biosensor for Hg2+ [81]. The base modifications in 10-13 DNAzyme limited its application in biosensor design. Thus, few biosensors had been reported based on Hg2+-specific DNAzyme. Most DNAzyme biosensors for Hg2+ are based on other modified DNAzymes such as UO22+-ion-specific DNAzyme, Cu2+-specific DNAzyme, and Mg2+-specific DNAzyme (Figure 8) [31,82,83,84].

3.1. UO22+-Specific DNAzyme

The Lu group designed an ultrahigh sensitivity and selectivity Hg2+ biosensor based on modified UO22+-ion-specific DNAzyme [18]. The originally UO22+-ion-specific DNAzyme contains a substrate strand (39S) and an enzyme strand (39E) which contains an eight-nucleotide bulge and a stem loop [87]. This group found that changing the base of the stem loop had no effect on the activity and the role of stem loop was only structural maintenance. When the stem loop was replaced and one of the A·G mismatches on the left side of cleavage site was replaced by an A-T base pair to form EHg0T, the new DNAzyme was still active in the presence of UO22+-ion. Then, other mutant DNAzyme with different amounts of T-T mismatches in the stem region was tested to observe the enzyme activity. Because EHg5T had no activity in the absence of Hg2+, EHg5T was chosen to design Hg2+ biosensor (Figure 9a). At the beginning, the substrate 39S was labeled by the fluorophore and quencher. At one end close to the fluorophore, the new DNAzyme was also modified by the quencher to further quench the fluorescence. Thus, no fluorescence signal was observed without Hg2+. In the presence of Hg2+, Hg2+ folded the new DNAzyme into an active conformation. With UO22+-ion, the new DNAzyme could cleave its substrate to release fluorescence (Figure 9b). Since the new DNAzyme was not damaged, it could enter the next cycle to bind with another substrate, releasing more fluorescence. The detection limit of this biosensor was 2.4 nM.

3.2. Cu2+-Specific DNAzyme

Zhang et al. developed an Hg2+ biosensor based on the Cu2+-specific DNAzyme and G-quadruplex DNAzymes [85]. Similar to the UO22+-ion-specific DNAzyme, they engineered the Cu2+-specific DNAzyme to recognize Hg2+. The originally Cu2+-specific DNAzyme was shown in Figure 10b. The T-A Watson-Crick base pair in the 5′-end of DNAzyme was replaced by a T·T mismatches to construct modified new DNAzyme (Figure 10d). Without Hg2+, the new DNAzyme could not associate with the substrate strand to form a stable enzyme/substrate complex. Thus, the substrate was free from being cleaved. The design strategy of this biosensor was shown in Figure 10a. A hairpin DNA contained a G-rich sequence and a substrate sequence was used in this biosensor. At the beginning, the G-rich sequence was covered by forming hairpin structure. Thus, the G-quadruplex DNAzyme could not be formed to oxidize ABTS color reaction. In the presence of Hg2+, the new DNAzyme could bind the substrate via T-Hg-T mismatch. Then, the hairpin substrate was cut in the presence of Cu2+. As a result, the G-rich sequence was released to form G-quadruplex DNAzymes which improved the oxidation activity of Hemin [88,89,90]. Then, ABTS was oxidized to produce the color. Meanwhile, the new DNAzyme entered the next cycle to split another hairpin substrate. The sensitivity of this biosensor was improved by DNA/RNA-cleaving DNAzyme and the G-quadruplex DNAzyme. Therefore, this biosensor had a high level of sensitivity with the detection limit of 4 nM.

3.3. Mg2+-Specific DNAzyme

As early as 1995, Breaker and Joyce obtained the Mg2+-dependent DNAzyme by in vitro selection [91]. This DNAzyme has high catalytic activity. Meanwhile, Mg2+ is a very common ion and is not harmful to the environment. Thus, modified Mg2+-dependent DNAzyme is well adapted to detect mercury ions. Qi, et al. designed a fluorescence DNA biosensor to detect Hg2+ based on split Mg2+-dependent DNAzyme [86]. In this biosensor, the Mg2+-dependent DNAzyme was artificially split into two separate fragments (probe1 and probe2). The T-rich sequence was added at the 5′-end of probe1 and the 3′-end of probe2. Meanwhile, the hairpin structure substrate with fluorescence and quencher was designed (Figure 11a). In the absence of Hg2+, the split Mg2+-dependent DNAzyme had no activity, and the substrate could not be cut. Thus, no fluorescent signal emitted. In the presence of Hg2+, probe1 and probe2 could combine to form a complete DNAzyme via T-Hg-T mismatch. With Mg2+, the hairpin substrate was cleaved to cause the separation of the fluorophore and the quencher. Therefore, the fluorescent signal could be recorded. After that probe1 and probe2 was released, the DNAzyme entered the next cycle to cleave another substrate. Then, stronger fluorescence could be observed. The detection limit of this amplified fluorescence biosensor was down to 0.2 nM.
In 2018, Deng et al. developed a visual and sensitive DNA biosensor for Hg2+ detection based on split DNAzyme amplification and peroxidase-like activity of hemin-graphene composites (H-GNs) [92]. In this biosensor, two split DNAzyme sequences were designed which contained partly E-DNA sequences at both ends and thymine bases in the middle. With the help of Hg2+, two entire E-DNA could be formed via T-Hg-T mismatch. Then, the entire E-DNA with high activity could cleave its molecular beacon (MB) substrate to result DNA fragments in the presence of Mg2+. When the DNA fragments were released, the E-DNA can hybridize with another MB substrate to cause more DNA fragments. The large amount of DNA fragments adsorbed on the surface of H-GNs to prevent forming aggregation. Then, TMB could be oxidized to produce color (Figure 11b). Without Hg2+, the split DNAzyme could not cleave MB substrate. Without the protection of DNA fragments, H-GNs would aggregate to lose peroxidase-like activity. Then, no color reaction happened. This visual and DNAzyme amplified biosensor had a low detection limit of 33 pM.
In 2018, Yun et al. reported a simple and amplified Hg2+ detection strategy based on DNAzyme motor [93]. In this biosensor, fluorophore labeled DNA probes and long arm DNA were modified on the surface of AuNPs via Au-S bond. The fluorophore-labeled DNA probes contained the substrate of Mg2+-specific DNAzyme. At the initial status, the fluorescent signal was quenched. The long arm DNA had a split E-DNA which was separated by T-rich sequence. In the absence of Hg2+, the split E-DNA had no activity and the fluorophore-labeled substrate could not be cleaved. Thus, no fluorescent signal could be observed. When Hg2+ was added, the split E-DNA was able to form an entire E-DNA via T-Hg-T interaction. Then the substrate was cleaved to release fluorophore in the presence of Mg2+. The free entire E-DNA could hybridize with another substrate to trigger the next cycle (Figure 11c). At last, more fluorophore molecules were released to bring significant fluorescent signal. The limit of detection of this biosensor was 30 pM.
Cai; et al. developed an electrochemical impedance biosensor for Hg2+ detection based on DNAzyme-assisted target recycling and hybridization chain reaction (HCR) [94]. In this biosensor, four hairpins DNA (H1, H2, H3, and H4) and a split Mg2+-specific DNAzyme were designed. The capture probe H1 was modified on the surface of GCE/AuNPs electrode. H2 contained the substrate sequence of DNAzyme. H3 and H4 were synthesized from two different copolymer chains P1 and P2 by acrylamide polymer, respectively. In the presence of Hg2+, the split DNAzyme could form an active entire DNAzyme. This entire DNAzyme could cleave H2 to release the partial substrate strand (sDNA) in the presence of Mg2+. Similar to the method above, DNAzyme was reused to cleave H2 thus to obtain more sDNA. Subsequently, sDNA could hybridize with H1 to open the hairpin structure. As a result, the terminal of H1 exposed, which could hybridize with P1 to open the hairpin structure of P1. Then, the terminal of P1 further hybridized with P2 to open the hairpin structure of P2. The HCR between P1 and P2 was initiated to assemble a nonconductive DNA hydrogel film on the surface of the electrode (Figure 11d). Thus, the electronic transfer was greatly hindered. By measuring the impedance signal, the ultrasensitive biosensor of Hg2+ was obtained with a low detection limit of 0.042 pM.

4. Applications of Hg2+ Biosensors in Real Samples

With good detection mechanism, these Hg2+ DNA biosensors were also applied in real samples to evaluate the reliability and applicability. Most of these biosensors performed high selectivity in the detection process due to the specificity of T-Hg-T mismatch (Table 2). A colorimetric biosensor based on Exo III-assisted target recycling with one cycle and gold nanoparticles was used to detect Hg2+ in tap water samples and lake water samples by Hong et al. [46]. By determining the recovery of spiked Hg2+, the values of the recovery were between 92% and 106%. Meanwhile, the results were identical to those obtained by ICP-MS. The above data indicated that this biosensor had favorable potential to be applied in real samples. The electrochemical based on Exo III-assisted target recycling with two cycles was applied to detect Hg2+ in the tap water by Song et al. [51]. Three water samples were prepared by adding different concentrations of Hg2+ (10, 100, 1000 nM). Then the concentration of Hg2+ was measured by this biosensor with the linear range of 500 pM–5 μM and the standard atomic fluorescence spectroscopy (AFS). The results showed that this biosensor was in good agreement with AFS and the discrepancies between the two methods were all less than 14.2%. These results revealed that this biosensor might hold great potential for real sample detection. Liu et al. designed a biosensor based on nickase-assisted signal amplification to detect Hg2+ in in the tap water [68]. Initially, the tap was wrapped with a 0.22 mm membrane to filter the water. Then, the tap water was spiked with different concentrations of Hg2+. Finally, Hg2+ was quantitatively detected by the linear equation of the proposed biosensor. The recovery values were in the range of 94.2–111.4%, and the relative standard deviation (RSD) was between 3.8–5.0%. These results showed that this biosensor was satisfactory in monitoring the tap water. Qi developed a biosensor based on Mg2+-specific DNAzyme to test Hg2+ in Xi’an Chan River containing a variety of interference [86]. At the beginning, the river water samples were simply filtered to remove the insoluble substances. Then, the spiked water samples were prepared with different concentrations of Hg2+. At last, the level of Hg2+ was measured. The recoveries of this biosensor were between 96% and 105%. The results indicated that no obvious Hg2+ contamination was found in the Xi’an Chan River and the proposed biosensor could accurately measure Hg2+ in real samples.

5. Summary and Future Perspectives

In this article, we reviewed the enzyme-driven signal amplification strategy in the construction of DNA biosensors for Hg2+ detection. The enzymes were divided into nucleases and DNAzymes according to their chemical nature. The component of nucleases is protein, while DNAzymes consist of nucleic acids. By contrast, DNA is more stable, cheaper, and easier to modify than protein. However, a wide variety of nucleases are available for designing Hg2+ biosensor including Exo III, Exo I, Nickase, DSN, and DNase I. In the nucleases section, the Exo III-driven signal amplification strategy was introduced in detail. Since Hg2+ can help ssDNA fold into dsDNA via T-Hg-T, and the substrate of Exo III is dsDNA, Exo III can be used to design Hg2+ biosensor flexibly. In the DNAzymes section, it is difficult to obtain Hg2+-specific DNAzyme. Most of the DNAzymes used in Hg2+ biosensor are modified from DNAzymes which are specific for other metal ions, for example, the Mg2+-specific DNAzyme. These approaches with the help of other metal ion-specific DNAzyme provide a new way to design biosensors. The biosensors based on different enzymes were compared in Table 2. In ion specificity, they were all highly selective with the same recognition mechanism based on T-Hg-T mismatch. In sensitivity, the detection limit of Exo III with one cycle was range from 1 pM–380 pM. When another cycle was introduced, the detection limit can be improved to 10 fM. The highest sensitivity with the detection limit of 0.19 fM could be obtained when the nanoflowers were used in combination with Exo III. Exo I performed slightly less effective. However, when it is combined with microscope, the sensitivity can be greatly improved. The detection limit of nickase is 0.8 nM–1.7 nM. When it is combined with other enzymes such as TdTase, the sensitivity can also be remarkably improved. For example, DSN has a satisfactory sensitivity 10 fM. The sensitivity of DNase I, UO22+-ion-specific DNAzyme and Cu2+-specific DNAzyme is similar to that of nickase. Moreover, the Mg2+-specific DNAzyme shows the same sensitivity as Exo III. The sensitivity of Mg2+-specific DNAzyme can also be increased with other amplification strategy such as HCR (Table 2). In summary, the sensitivity of the developed methods can fully meet the requirements of Hg2+ detection in drinking water (MRL 10 nM). The Exo III, DSN and Mg2+-specific DNAzymes have high sensitivity. The nickase, DNase I, UO22+-ion-specific DNAzyme and Cu2+-specific DNAzyme have a moderate sensitivity. Therefore, when we design Hg2+ biosensor based on enzyme-driven signal amplification strategy in the near future, it will be better to select Exo III, DSN and Mg2+-specific DNAzyme as tool enzymes. Meanwhile, it is worth noting that increasing cycle, combining with nano-materials, instrument, other enzymes and other amplification strategy will improve the sensitivity of the biosensors. Thus, one future direction may focus on how to combine other ways to improve the sensitivity. The second future direction is to detect methyl mercury. Methyl mercury is another form of mercury, and this form is much more toxic which can cause permanent damage to the brain. However, the biosensors for methyl mercury have been reported much fewer [95,96,97]. This is a challenge for all the researchers in this filed. The third future direction is the simultaneous detection of multiple metal ions [98,99,100]. Since more than one toxic metal ion should be detected for ensuring people’s health, simultaneous detection of multiple ions will greatly save cost and time.

Funding

This research received no external funding.

Data Availability Statement

The datasets used and/or analyzed and reported in this review are available from the corresponding author on reasonable request.

Conflicts of Interest

The author declares no conflict of interest.

References

  1. Boening, D.W. Ecological effects, transport, and fate of mercury: A general review. Chemosphere 2000, 40, 1335–1351. [Google Scholar] [CrossRef]
  2. Renzoni, A.; Zino, F.; Franchi, E. Mercury levels along the food chain and risk for exposed populations. Environ. Res. 1998, 77, 68–72. [Google Scholar] [CrossRef]
  3. Malm, O. Gold mining as a source of mercury exposure in the Brazilian Amazon. Environ. Res. 1998, 77, 73–78. [Google Scholar] [CrossRef] [PubMed]
  4. Joensuu, O.I. Fossil fuels as a source of mercury pollution. Science 1971, 172, 1027–1028. [Google Scholar] [CrossRef]
  5. Clarkson, T.W. Mercury: Major issues in environmental health. Environ. Health Perspect. 1993, 100, 31–38. [Google Scholar] [CrossRef] [PubMed]
  6. Onyido, I.; Norris, A.R.; Buncel, E. Biomolecule--mercury interactions: Modalities of DNA base--mercury binding mechanisms. Remediation strategies. Chem. Rev. 2004, 104, 5911–5929. [Google Scholar] [CrossRef]
  7. Valko, M.; Morris, H.; Cronin, M.T. Metals, toxicity and oxidative stress. Curr. Med. Chem. 2005, 12, 1161–1208. [Google Scholar] [CrossRef] [Green Version]
  8. Nolan, E.M.; Lippard, S.J. Tools and tactics for the optical detection of mercuric ion. Chem. Rev. 2008, 108, 3443–3480. [Google Scholar] [CrossRef]
  9. Clarkson, T.W.; Magos, L.; Myers, G.J. The toxicology of mercury--current exposures and clinical manifestations. N. Engl. J. Med. 2003, 349, 1731–1737. [Google Scholar] [CrossRef] [Green Version]
  10. Aramendia, M.; Guarda, A.; Leite, D.; Resano, M. Direct mercury determination in blood and urine by means of high-resolution continuum source graphite furnace atomic absorption spectrometry using gold nanoparticles as a chemical modifier. J. Ana. Atom. Spectrom. 2017, 32, 2352–2359. [Google Scholar] [CrossRef]
  11. Panichev, N.A.; Panicheva, S.E. Determination of total mercury in fish and sea products by direct thermal decomposition atomic absorption spectrometry. Food Chem. 2015, 166, 432–441. [Google Scholar] [CrossRef]
  12. Chen, J.; Chakravarty, P.; Davidson, G.R.; Wren, D.G.; Locke, M.A.; Zhou, Y.; Brown, G.; Cizdziel, J.V. Simultaneous determination of mercury and organic carbon in sediment and soils using a direct mercury analyzer based on thermal decomposition-atomic absorption spectrophotometry. Anal. Chim. Acta 2015, 871, 9–17. [Google Scholar] [CrossRef]
  13. Nolan, E.M.; Lippard, S.J. A “Turn-On” fluorescent sensor for the selective detection of mercuric ion in aqueous media. J. Am. Chem. Soc. 2003, 125, 14270–14271. [Google Scholar] [CrossRef]
  14. Moon, S.Y.; Youn, N.J.; Park, S.M.; Chang, S.K. Diametrically disubstituted cyclam derivative having Hg2+-selective fluoroionophoric behaviors. J. Org. Chem. 2005, 70, 2394–2397. [Google Scholar] [CrossRef]
  15. Yang, Y.; Jiang, J.H.; Shen, G.L.; Yu, R.Q. An optical sensor for mercury ion based on the fluorescence quenching of tetra(p-dimethylaminophenyl)porphyrin. Anal. Chim. Acta 2009, 636, 83–88. [Google Scholar] [CrossRef] [PubMed]
  16. Wegner, S.V.; Okesli, A.; Chen, P.; He, C. Design of an emission ratiometric biosensor from MerR family proteins: A sensitive and selective sensor for Hg2+. J. Am. Chem. Soc. 2007, 129, 3474–3475. [Google Scholar] [CrossRef]
  17. Liu, M.; Wang, Z.; Pan, L.; Cui, Y.; Liu, Y. A SERS/fluorescence dual-mode nanosensor based on the human telomeric G-quadruplex DNA: Application to mercury (II) detection. Biosens. Bioelectron. 2015, 69, 142–147. [Google Scholar] [CrossRef]
  18. Liu, J.; Lu, Y. Rational design of “turn-on” allosteric DNAzyme catalytic beacons for aqueous mercury ions with ultrahigh sensitivity and selectivity. Angew. Chem. Int. Ed. Engl. 2007, 46, 7587–7590. [Google Scholar] [CrossRef]
  19. Tortolini, C.; Bollella, P.; Antonelli, M.L.; Antiochia, R.; Mazzei, F.; Favero, G. DNA-based biosensors for Hg2+ determination by polythymine-methylene blue modified electrodes. Biosens. Bioelectron. 2015, 67, 524–531. [Google Scholar] [CrossRef]
  20. Ono, A.; Togashi, H. Highly selective oligonucleotide-based sensor for mercury(II) in aqueous solutions. Angew. Chem. Int. Ed. Engl. 2004, 43, 4300–4302. [Google Scholar] [CrossRef]
  21. Miyake, Y.; Togashi, H.; Tashiro, M.; Yamaguchi, H.; Oda, S.; Kudo, M.; Tanaka, Y.; Kondo, Y.; Sawa, R.; Fujimoto, T.; et al. MercuryII-mediated formation of thymine-HgII-thymine base pairs in DNA duplexes. J. Am. Chem. Soc. 2006, 128, 2172–2173. [Google Scholar] [CrossRef]
  22. Tanaka, Y.; Oda, S.; Yamaguchi, H.; Kondo, Y.; Kojima, C.; Ono, A. 15N-15N J-coupling across Hg(II): Direct observation of Hg(II)-mediated T-T base pairs in a DNA duplex. J. Am. Chem. Soc. 2007, 129, 244–245. [Google Scholar] [CrossRef]
  23. Wang, Z.; Heon Lee, J.; Lu, Y. Highly sensitive “turn-on” fluorescent sensor for Hg2+ in aqueous solution based on structure-switching DNA. Chem. Commun. (Camb.) 2008, 6005–6007. [Google Scholar] [CrossRef]
  24. Chen, G.H.; Chen, W.Y.; Yen, Y.C.; Wang, C.W.; Chang, H.T.; Chen, C.F. Detection of mercury(II) ions using colorimetric gold nanoparticles on paper-based analytical devices. Anal. Chem. 2014, 86, 6843–6849. [Google Scholar] [CrossRef]
  25. Liu, J.; Chen, L.B.; Chen, J.H.; Ge, C.C.; Fang, Z.Y.; Wang, L.; Xing, X.R.; Zeng, L.W. An autonomous T-rich DNA machine based lateral flow biosensor for amplified visual detection of mercury ions. Anal. Methods 2014, 6, 2024–2027. [Google Scholar] [CrossRef]
  26. Ding, B.; Liu, C.; Wu, Q.; Wang, Y.; Li, L.; Yang, H. A Label-free and Highly Sensitive Fluorescence Strategy for Mercury Ion Detection Based on Exonuclease III-aided Recycling Amplification. Anal. Sci. 2018, 34, 259–261. [Google Scholar] [CrossRef] [Green Version]
  27. Zhong, Y.Q.; Ning, T.J.; Cheng, L.; Xiong, W.; Wei, G.B.; Liao, F.S.; Ma, G.Q.; Hong, N.; Cui, H.F.; Fan, H. An electrochemical Hg(2+) sensor based on signal amplification strategy of target recycling. Talanta 2021, 223, 121709. [Google Scholar] [CrossRef]
  28. Li, D.; Yang, F.; Li, X.; Yuan, R.; Xiang, Y. Target-mediated base-mismatch initiation of a non-enzymatic signal amplification network for highly sensitive sensing of Hg(2). Analyst 2020, 145, 507–512. [Google Scholar] [CrossRef] [PubMed]
  29. Xu, A.; Chao, L.; Xiao, H.; Sui, Y.; Liu, J.; Xie, Q.; Yao, S. Ultrasensitive electrochemical sensing of Hg(2+) based on thymine-Hg(2+)-thymine interaction and signal amplification of alkaline phosphatase catalyzed silver deposition. Biosens. Bioelectron. 2018, 104, 95–101. [Google Scholar] [CrossRef]
  30. Qi, Y.; Xiu, F.R.; Yu, G.; Huang, L.; Li, B. Simple and rapid chemiluminescence aptasensor for Hg(2+) in contaminated samples: A new signal amplification mechanism. Biosens. Bioelectron. 2017, 87, 439–446. [Google Scholar] [CrossRef]
  31. Chen, J.; Pan, J.; Chen, S. A naked-eye colorimetric sensor for Hg(2+) monitoring with cascade signal amplification based on target-induced conjunction of split DNAzyme fragments. Chem. Commun. (Camb.) 2017, 53, 10224–10227. [Google Scholar] [CrossRef]
  32. Liu, T.; Chu, Z.Y.; Jin, W.Q. Electrochemical mercury biosensors based on advanced nanomaterials. J. Mater. Chem. B 2019, 7, 3620–3632. [Google Scholar] [CrossRef]
  33. Li, L.Y.; Wen, Y.L.; Xu, L.; Xu, Q.; Song, S.P.; Zuo, X.L.; Yan, J.; Zhang, W.J.; Liu, G. Development of mercury (II) ion biosensors based on mercury-specific oligonucleotide probes. Biosens. Bioelectron. 2016, 75, 433–445. [Google Scholar] [CrossRef]
  34. Sahin, S.; Caglayan, M.O.; Ustundag, Z. A review on nanostructure-based mercury (II) detection and monitoring focusing on aptamer and oligonucleotide biosensors. Talanta 2020, 220, 121437. [Google Scholar] [CrossRef] [PubMed]
  35. Xia, N.; Feng, F.; Liu, C.; Li, R.Q.; Xiang, W.W.; Shi, H.X.; Gao, L. The detection of mercury ion using DNA as sensors based on fluorescence resonance energy transfer. Talanta 2019, 192, 500–507. [Google Scholar] [CrossRef]
  36. Qing, T.P.; He, D.G.; He, X.X.; Wang, K.M.; Xu, F.Z.; Wen, L.; Shangguan, J.F.; Mao, Z.G.; Lei, Y.L. Nucleic acid tool enzymes-aided signal amplification strategy for biochemical analysis: Status and challenges. Anal. Bioanal. Chem. 2016, 408, 2793–2811. [Google Scholar] [CrossRef]
  37. Yan, M.; Bai, W.; Zhu, C.; Huang, Y.; Yan, J.; Chen, A. Design of nuclease-based target recycling signal amplification in aptasensors. Biosens. Bioelectron. 2016, 77, 613–623. [Google Scholar] [CrossRef]
  38. Miao, P.; Tang, Y.G.; Wang, B.D.; Yin, J.; Ning, L.M. Signal amplification by enzymatic tools for nucleic acids. Trac-Trend. Anal. Chem. 2015, 67, 1–15. [Google Scholar] [CrossRef]
  39. Ravikumar, A.; Panneerselvam, P. Polydopamine nanotube mediated fluorescent biosensor for Hg(ii) determination through exonuclease III-assisted signal amplification. Analyst 2018, 143, 2623–2631. [Google Scholar] [CrossRef]
  40. Ravikumar, A.; Panneerselvam, P.; Morad, N. Metal-Polydopamine Framework as an Effective Fluorescent Quencher for Highly Sensitive Detection of Hg(II) and Ag(I) Ions through Exonuclease III Activity. ACS Appl. Mater. Interfaces 2018, 10, 20550–20558. [Google Scholar] [CrossRef] [PubMed]
  41. Ning, Y.; Hu, J.; Wei, K.; He, G.; Wu, T.; Lu, F. Fluorometric determination of mercury(II) via a graphene oxide-based assay using exonuclease III-assisted signal amplification and thymidine-Hg(II)-thymidine interaction. Microchim. Acta 2019, 186, 216. [Google Scholar] [CrossRef]
  42. Zhang, H.; Guan, Y.; Li, X.; Lian, L.; Wang, X.; Gao, W.; Zhu, B.; Liu, X.; Lou, D. Ultrasensitive Biosensor for Detection of Mercury(II) Ions Based on DNA-Cu Nanoclusters and Exonuclease III-assisted Signal Amplification. Anal. Sci. 2018, 34, 1155–1161. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  43. Ma, H.; Xue, N.; Wu, S.; Li, Z.; Miao, X. Fluorometric determination of mercury(II) using positively charged gold nanoparticles, DNA-templated silver nanoclusters, T-Hg(II)-T interaction and exonuclease assisted signal amplification. Microchim. Acta 2019, 186, 317. [Google Scholar] [CrossRef]
  44. Yang, H.L.; Zhou, Y.; Liu, J.W. G-quadruplex DNA for construction of biosensors. Trac-Trend. Anal. Chem. 2020, 132, 116060. [Google Scholar] [CrossRef]
  45. Zhu, Q.; Liu, L.; Xing, Y.; Zhou, X. Duplex functional G-quadruplex/NMM fluorescent probe for label-free detection of lead(II) and mercury(II) ions. J. Hazard. Mater. 2018, 355, 50–55. [Google Scholar] [CrossRef] [PubMed]
  46. Hong, M.; Zeng, B.; Li, M.; Xu, X.; Chen, G. An ultrasensitive conformation-dependent colorimetric probe for the detection of mercury(II) using exonuclease III-assisted target recycling and gold nanoparticles. Microchim. Acta 2017, 185, 72. [Google Scholar] [CrossRef]
  47. Fu, C.; Yu, H.; Su, L.; Liu, C.; Song, Y.; Wang, S.; Lin, Z.; Chen, F. A homogeneous electrochemical sensor for Hg(2+) determination in environmental water based on the T-Hg(2+)-T structure and exonuclease III-assisted recycling amplification. Analyst 2018, 143, 2122–2127. [Google Scholar] [CrossRef]
  48. Zhang, H.; Lei, Z.X.; Fu, X.; Deng, X.C.; Wang, Q.; Gu, D.Y. Hg2+-triggered exonuclease III-assisted dual-cycle targets recycling amplification for label-free and ultrasensitive colorimetric detection of Hg2+. Sens. Actuators B-Chem. 2017, 246, 896–903. [Google Scholar] [CrossRef]
  49. Zhang, Z.H.; Zhang, F.; He, P.; Zhang, X.R.; Song, W.L. Fluorometric determination of mercury(II) by using thymine-thymine mismatches as recognition elements, toehold binding, and enzyme-assisted signal amplification. Microchim. Acta 2019, 186, 551. [Google Scholar] [CrossRef]
  50. Song, X.; Wang, Y.; Liu, S.; Zhang, X.; Wang, H.; Wang, J.; Huang, J. Colorimetric and visual mercury(II) assay based on target-induced cyclic enzymatic amplification, thymine-Hg(II)-thymine interaction, and aggregation of gold nanoparticles. Microchim. Acta 2019, 186, 105. [Google Scholar] [CrossRef] [PubMed]
  51. Song, X.; Wang, Y.; Liu, S.; Zhang, X.; Wang, H.; Wang, J.; Huang, J. Ultrasensitive electrochemical detection of Hg(2+) based on an Hg(2+)-triggered exonuclease III-assisted target recycling strategy. Analyst 2018, 143, 5771–5778. [Google Scholar] [CrossRef]
  52. Zhou, D.; Zeng, L.; Pan, J.; Li, Q.; Chen, J. Autocatalytic DNA circuit for Hg(2+) detection with high sensitivity and selectivity based on exonuclease III and G-quadruplex DNAzyme. Talanta 2020, 207, 120258. [Google Scholar] [CrossRef]
  53. Huang, H.; Shi, S.; Zheng, X.; Yao, T. Sensitive detection for coralyne and mercury ions based on homo-A/T DNA by exonuclease signal amplification. Biosens. Bioelectron. 2015, 71, 439–444. [Google Scholar] [CrossRef]
  54. He, W.; Qiao, B.; Li, F.; Pan, L.; Chen, D.; Cao, Y.; Tu, J.; Wang, X.; Lv, C.; Wu, Q. A novel electrochemical biosensor for ultrasensitive Hg(2+) detection via a triple signal amplification strategy. Chem. Commun. (Camb.) 2021, 57, 619–622. [Google Scholar] [CrossRef]
  55. Yuan, M.; Zhu, Y.; Lou, X.; Chen, C.; Wei, G.; Lan, M.; Zhao, J. Sensitive label-free oligonucleotide-based microfluidic detection of mercury (II) ion by using exonuclease I. Biosens. Bioelectron. 2012, 31, 330–336. [Google Scholar] [CrossRef]
  56. Li, Y.; Liu, Q.; Chen, Z. Optical aptasensing of mercury(II) by using salt-induced and exonuclease I-induced gold nanoparticle aggregation under dark-field microscope observation. Microchim. Acta 2019, 186, 729. [Google Scholar] [CrossRef] [PubMed]
  57. Yin, X.; Chen, B.; He, M.; Hu, B. A Multifunctional Platform for the Capture, Release, And Enumeration of Circulating Tumor Cells Based on Aptamer Binding, Nicking Endonuclease-Assisted Amplification, And Inductively Coupled Plasma Mass Spectrometry Detection. Anal. Chem. 2020, 92, 10308–10315. [Google Scholar] [CrossRef]
  58. Wang, Y.; Bai, J.; Huo, B.; Yuan, S.; Zhang, M.; Sun, X.; Peng, Y.; Li, S.; Wang, J.; Ning, B.; et al. Upconversion Fluorescent Aptasensor for Polychlorinated Biphenyls Detection Based on Nicking Endonuclease and Hybridization Chain Reaction Dual-Amplification Strategy. Anal. Chem. 2018, 90, 9936–9942. [Google Scholar] [CrossRef]
  59. Yang, L.; Tao, Y.; Yue, G.; Li, R.; Qiu, B.; Guo, L.; Lin, Z.; Yang, H.H. Highly Selective and Sensitive Electrochemiluminescence Biosensor for p53 DNA Sequence Based on Nicking Endonuclease Assisted Target Recycling and Hyperbranched Rolling Circle Amplification. Anal. Chem. 2016, 88, 5097–5103. [Google Scholar] [CrossRef]
  60. Wang, G.L.; Fang, X.; Wu, X.M.; Hu, X.L.; Li, Z.J. Label-free and ratiometric detection of nuclei acids based on graphene quantum dots utilizing cascade amplification by nicking endonuclease and catalytic G-quadruplex DNAzyme. Biosens. Bioelectron. 2016, 81, 214–220. [Google Scholar] [CrossRef] [PubMed]
  61. Hong, M.; Wang, M.; Wang, J.; Xu, X.; Lin, Z. Ultrasensitive and selective electrochemical biosensor for detection of mercury (II) ions by nicking endonuclease-assisted target recycling and hybridization chain reaction signal amplification. Biosens. Bioelectron. 2017, 94, 19–23. [Google Scholar] [CrossRef] [PubMed]
  62. Zhang, Y.; Li, S.; Tian, J.; Li, K.; Du, Z.; Xu, W. Universal linker Polymerase Chain Reaction-triggered Strand Displacement Amplification visual biosensor for ultra-sensitive detection of Salmonella. Talanta 2021, 222, 121575. [Google Scholar] [CrossRef] [PubMed]
  63. Xue, L.Y.; Zhou, X.M.; Xing, D. Sensitive and Homogeneous Protein Detection Based on Target-Triggered Aptamer Hairpin Switch and Nicking Enzyme Assisted Fluorescence Signal Amplification. Anal. Chem. 2012, 84, 3507–3513. [Google Scholar] [CrossRef]
  64. Li, F.; Feng, Y.; Liu, S.; Tang, B. Triggered activity of a nicking endonuclease for mercuric(II) ion-mediated duplex-like DNA cleavage. Chem. Commun. (Camb.) 2011, 47, 6347–6349. [Google Scholar] [CrossRef] [PubMed]
  65. Ma, J.; Chen, Y.; Hou, Z.; Jiang, W.; Wang, L. Selective and sensitive mercuric (ii) ion detection based on quantum dots and nicking endonuclease assisted signal amplification. Biosens. Bioelectron. 2013, 43, 84–87. [Google Scholar] [CrossRef] [PubMed]
  66. Vijayan, A.N.; Liu, Z.; Zhao, H.; Zhang, P. Nicking enzyme-assisted signal-amplifiable Hg(2+) detection using upconversion nanoparticles. Anal. Chim. Acta 2019, 1072, 75–80. [Google Scholar] [CrossRef]
  67. Xie, H.; Wang, Q.; Chai, Y.Q.; Yuan, Y.L.; Yuan, R. Enzyme-assisted cycling amplification and DNA-templated in-situ deposition of silver nanoparticles for the sensitive electrochemical detection of Hg2+. Biosens. Bioelectron. 2016, 86, 630–635. [Google Scholar] [CrossRef] [PubMed]
  68. Liu, J.L.; Liu, L.P.; Chen, J.; Wang, T.C.; Xu, Y.Z.; Dai, Z.; Zou, X.Y. Selective and rapid detection of mercury ion based on DNA assembly and nicking endonuclease-assisted signal amplification. Anal. Methods 2019, 11, 3073–3078. [Google Scholar] [CrossRef]
  69. Ou, X.; Lou, X.; Xia, F. A highly sensitive DNA-AIEgen-based “turn-on” fluorescence chemosensor for amplification analysis of Hg2+ ions in real samples and living cells. Sci. China Chem. 2017, 60, 663–669. [Google Scholar] [CrossRef]
  70. Wei, Y.; Li, B.; Wang, X.; Duan, Y. A nano-graphite-DNA hybrid sensor for magnified fluorescent detection of mercury(II) ions in aqueous solution. Analyst 2014, 139, 1618–1621. [Google Scholar] [CrossRef] [Green Version]
  71. Tang, D.; Tang, J.; Li, Q.; Su, B.; Chen, G. Ultrasensitive aptamer-based multiplexed electrochemical detection by coupling distinguishable signal tags with catalytic recycling of DNase I. Anal. Chem. 2011, 83, 7255–7259. [Google Scholar] [CrossRef]
  72. Song, B.; Li, D.; Qi, W.P.; Elstner, M.; Fan, C.H.; Fang, H.P. Graphene on Au(111): A Highly Conductive Material with Excellent Adsorption Properties for High-Resolution Bio/Nanodetection and Identification. Chemphyschem 2010, 11, 585–589. [Google Scholar] [CrossRef] [PubMed]
  73. Lu, M.; Xiao, R.; Zhang, X.; Niu, J.; Zhang, X.; Wang, Y. Novel electrochemical sensing platform for quantitative monitoring of Hg(II) on DNA-assembled graphene oxide with target recycling. Biosens. Bioelectron. 2016, 85, 267–271. [Google Scholar] [CrossRef] [PubMed]
  74. Lu, C.H.; Li, J.A.; Lin, M.H.; Wang, Y.W.; Yang, H.H.; Chen, X.; Chen, G.N. Amplified Aptamer-Based Assay through Catalytic Recycling of the Analyte. Angew. Chem. Int. Ed. 2010, 49, 8454–8457. [Google Scholar] [CrossRef]
  75. Kruger, K.; Grabowski, P.J.; Zaug, A.J.; Sands, J.; Gottschling, D.E.; Cech, T.R. Self-splicing RNA: Autoexcision and autocyclization of the ribosomal RNA intervening sequence of Tetrahymena. Cell 1982, 31, 147–157. [Google Scholar] [CrossRef]
  76. Breaker, R.R.; Joyce, G.F. A DNA enzyme that cleaves RNA. Chem. Biol. 1994, 1, 223–229. [Google Scholar] [CrossRef]
  77. Li, J.; Lu, Y. A highly sensitive and selective catalytic DNA biosensor for lead ions. J. Am. Chem. Soc. 2000, 122, 10466–10467. [Google Scholar] [CrossRef]
  78. Yu, T.M.; Zhou, W.H.; Liu, J.W. Screening of DNAzyme mutants for highly sensitive and selective detection of calcium in milk. Anal. Methods 2018, 10, 1740–1746. [Google Scholar] [CrossRef]
  79. Ren, W.; Huang, P.J.J.; de Rochambeau, D.; Moon, W.J.; Zhang, J.Y.; Lyu, M.S.; Wang, S.J.; Sleiman, H.; Liu, J.W. Selection of a metal ligand modified DNAzyme for detecting Ni2+. Biosens. Bioelectron. 2020, 165, 112285. [Google Scholar] [CrossRef]
  80. Huang, P.J.J.; Liu, J.W. In vitro Selection of Chemically Modified DNAzymes. Chemistryopen 2020, 9, 1046–1059. [Google Scholar] [CrossRef]
  81. Hollenstein, M.; Hipolito, C.; Lam, C.; Dietrich, D.; Perrin, D.M. A highly selective DNAzyme sensor for mercuric ions. Angew. Chem. Int. Ed. Engl. 2008, 47, 4346–4350. [Google Scholar] [CrossRef]
  82. Shimron, S.; Elbaz, J.; Henning, A.; Willner, I. Ion-induced DNAzyme switches. Chem. Commun. 2010, 46, 3250–3252. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  83. Li, Y.; Chang, Y.; Ma, J.; Wu, Z.; Yuan, R.; Chai, Y. Programming a Target-Initiated Bifunctional DNAzyme Nanodevice for Sensitive Ratiometric Electrochemical Biosensing. Anal. Chem. 2019, 91, 6127–6133. [Google Scholar] [CrossRef] [PubMed]
  84. Li, X.; Xie, J.; Jiang, B.; Yuan, R.; Xiang, Y. Metallo-Toehold-Activated Catalytic Hairpin Assembly Formation of Three-Way DNAzyme Junctions for Amplified Fluorescent Detection of Hg(2). ACS Appl. Mater. Interfaces 2017, 9, 5733–5738. [Google Scholar] [CrossRef]
  85. Zhang, Q.; Cai, Y.; Li, H.; Kong, D.-M.; Shen, H.-X. Sensitive dual DNAzymes-based sensors designed by grafting self-blocked G-quadruplex DNAzymes to the substrates of metal ion-triggered DNA/RNA-cleaving DNAzymes. Biosens. Bioelectron. 2012, 38, 331–336. [Google Scholar] [CrossRef]
  86. Qi, L.; Zhao, Y.; Yuan, H.; Bai, K.; Zhao, Y.; Chen, F.; Dong, Y.; Wu, Y. Amplified fluorescence detection of mercury(II) ions (Hg2+) using target-induced DNAzyme cascade with catalytic and molecular beacons. Analyst 2012, 137, 2799–2805. [Google Scholar] [CrossRef] [PubMed]
  87. Liu, J.; Brown, A.K.; Meng, X.; Cropek, D.M.; Istok, J.D.; Watson, D.B.; Lu, Y. A catalytic beacon sensor for uranium with parts-per-trillion sensitivity and millionfold selectivity. Proc. Natl. Acad. Sci. USA 2007, 104, 2056–2061. [Google Scholar] [CrossRef] [Green Version]
  88. Travascio, P.; Li, Y.; Sen, D. DNA-enhanced peroxidase activity of a DNA aptamer-hemin complex. Chem. Biol. 1998, 5, 505–517. [Google Scholar] [CrossRef] [Green Version]
  89. Wu, C.; Gao, G.; Zhai, K.; Xu, L.; Zhang, D. A visual Hg2+ detection strategy based on distance as readout by G-quadruplex DNAzyme on microfluidic paper. Food Chem. 2020, 127208. [Google Scholar] [CrossRef]
  90. Li, H.; Liu, M.; Zhao, W.; Pu, J.; Xu, J.; Wang, S.; Yu, R. Multi-channel collection of G-quadruplex transducers for amplified signaling of Pax-5 based on target-triggered split-to-intact remodeling of dual-G-rich duplex probe. Sensor. Actuat. B-Chem. 2020, 127913. [Google Scholar] [CrossRef]
  91. Breaker, R.R.; Joyce, G.F. A DNA enzyme with Mg(2+)-dependent RNA phosphoesterase activity. Chem. Biol. 1995, 2, 655–660. [Google Scholar] [CrossRef] [Green Version]
  92. Deng, P.; Zheng, S.; Yun, W.; Zhang, W.; Yang, L. A visual and sensitive Hg(2+) detection strategy based on split DNAzyme amplification and peroxidase-like activity of hemin-graphene composites. Spectrochim. Acta A Mol. Biomol. Spectrosc. 2019, 210, 335–340. [Google Scholar] [CrossRef] [PubMed]
  93. Yun, W.; Zhong, H.; Zheng, S.; Wang, R.; Yang, L. Simple, one-step and amplified Hg2+ detection strategy based on DNAzyme motor. Sens. Actuators B-Chem. 2018, 277, 456–461. [Google Scholar] [CrossRef]
  94. Cai, W.; Xie, S.; Zhang, J.; Tang, D.; Tang, Y. An electrochemical impedance biosensor for Hg(2+) detection based on DNA hydrogel by coupling with DNAzyme-assisted target recycling and hybridization chain reaction. Biosens. Bioelectron. 2017, 98, 466–472. [Google Scholar] [CrossRef] [PubMed]
  95. Oh, S.; Jeon, J.; Jeong, J.; Park, J.; Oh, E.T.; Park, H.J.; Lee, K.H. Fluorescent Detection of Methyl Mercury in Aqueous Solution and Live Cells Using Fluorescent Probe and Micelle Systems. Anal. Chem. 2020, 92, 4917–4925. [Google Scholar] [CrossRef]
  96. Chen, Z.; Li, P.; Cheng, X.; Yang, W.; Wu, Y.; Chen, Q.; Fu, F. Multicolor Aptasensor Based on DNA-Induced Au-Ag Nanorods for Simultaneous and Visual Detection of Inorganic and Organic Mercury. ACS Omega 2019, 4, 15112–15119. [Google Scholar] [CrossRef] [Green Version]
  97. Chen, Z.; Wang, X.; Cheng, X.; Yang, W.; Wu, Y.; Fu, F. Specifically and Visually Detect Methyl-Mercury and Ethyl-Mercury in Fish Sample Based on DNA-Templated Alloy Ag-Au Nanoparticles. Anal. Chem. 2018, 90, 5489–5495. [Google Scholar] [CrossRef]
  98. Xia, J.; Lin, M.; Zuo, X.; Su, S.; Wang, L.; Huang, W.; Fan, C.; Huang, Q. Metal ion-mediated assembly of DNA nanostructures for cascade fluorescence resonance energy transfer-based fingerprint analysis. Anal. Chem. 2014, 86, 7084–7087. [Google Scholar] [CrossRef] [PubMed]
  99. Sener, G.; Uzun, L.; Denizli, A. Colorimetric sensor array based on gold nanoparticles and amino acids for identification of toxic metal ions in water. ACS Appl. Mater. Interfaces 2014, 6, 18395–18400. [Google Scholar] [CrossRef]
  100. Yin, H.; Truskewycz, A.; Cole, I.S. Quantum dot (QD)-based probes for multiplexed determination of heavy metal ions. Microchim. Acta 2020, 187, 336. [Google Scholar] [CrossRef]
Figure 1. A scheme of different nucleases with different functions. Reprinted with permission from ref. [36]. Copyright 2015 Springer Nature.
Figure 1. A scheme of different nucleases with different functions. Reprinted with permission from ref. [36]. Copyright 2015 Springer Nature.
Biomolecules 11 00399 g001
Figure 2. (a) A scheme of fluorescence DNA biosensor to detect Hg2+ based on Exo III-assisted signal amplification and silver nanoclusters. Reprinted with permission from [43]. Copyright 2019 Springer Nature. (b) A scheme of a label-free fluorescence DNA biosensor for detection Hg2+ based on Exo III-aided signal amplification and G-quadruplex DNA [26]. (c) A scheme of a colorimetric DNA biosensor for the detection of Hg2+ using Exo III-assisted signal amplification and AuNPs. Reprinted with permission from [46]. Copyright 2017 Springer Nature. (d) A scheme of a homogeneous electrochemical DNA biosensor for Hg2+ determination based on Exo III-assisted recycling amplification and indium tin oxide (ITO) electrode. Reprinted with permission from [47]. Copyright 2018 Royal Society of Chemistry.
Figure 2. (a) A scheme of fluorescence DNA biosensor to detect Hg2+ based on Exo III-assisted signal amplification and silver nanoclusters. Reprinted with permission from [43]. Copyright 2019 Springer Nature. (b) A scheme of a label-free fluorescence DNA biosensor for detection Hg2+ based on Exo III-aided signal amplification and G-quadruplex DNA [26]. (c) A scheme of a colorimetric DNA biosensor for the detection of Hg2+ using Exo III-assisted signal amplification and AuNPs. Reprinted with permission from [46]. Copyright 2017 Springer Nature. (d) A scheme of a homogeneous electrochemical DNA biosensor for Hg2+ determination based on Exo III-assisted recycling amplification and indium tin oxide (ITO) electrode. Reprinted with permission from [47]. Copyright 2018 Royal Society of Chemistry.
Biomolecules 11 00399 g002
Figure 3. (a) A scheme of a colorimetric DNA biosensor for visual detection Hg2+ based on Exo III- driven twice cycles signal amplification strategy and AuNPs. Reprinted with permission from ref. [50]. Copyright 2019 Springer Nature. (b) A scheme of a ultrasensitive electrochemical for detection Hg2+ based on Exo III- assisted double cycles signal amplifi-cation strategy and gold electrodes. Reprinted with permission from ref. [51]. Copyright 2018 Royal Society of Chem-istry. (c) A scheme of a fluorescence DNA biosensor for Hg2+ detection based on G-quadruplex/NMM as a reporter. Reprinted with permission from ref. [52]. Copyright 2020 Elsevier. (d) A scheme of a triple signal amplification strategy for ultrasensitive Hg2+ detection. Reprinted with permission from ref. [54]. Copyright 2020 Royal Society of Chemistry.
Figure 3. (a) A scheme of a colorimetric DNA biosensor for visual detection Hg2+ based on Exo III- driven twice cycles signal amplification strategy and AuNPs. Reprinted with permission from ref. [50]. Copyright 2019 Springer Nature. (b) A scheme of a ultrasensitive electrochemical for detection Hg2+ based on Exo III- assisted double cycles signal amplifi-cation strategy and gold electrodes. Reprinted with permission from ref. [51]. Copyright 2018 Royal Society of Chem-istry. (c) A scheme of a fluorescence DNA biosensor for Hg2+ detection based on G-quadruplex/NMM as a reporter. Reprinted with permission from ref. [52]. Copyright 2020 Elsevier. (d) A scheme of a triple signal amplification strategy for ultrasensitive Hg2+ detection. Reprinted with permission from ref. [54]. Copyright 2020 Royal Society of Chemistry.
Biomolecules 11 00399 g003
Figure 4. (a) A scheme of a label-free fluorescence biosensor for detection of Hg2+ based on Exo I Reprinted with permission from [55]. Copyright 2012 Elsevier. (b) A scheme of an optical ultrasensitive DNA biosensor to detect Hg2+ based on dark-field microscope and Exo I. Reprinted with permission from [56]. Copyright 2019 Springer Nature.
Figure 4. (a) A scheme of a label-free fluorescence biosensor for detection of Hg2+ based on Exo I Reprinted with permission from [55]. Copyright 2012 Elsevier. (b) A scheme of an optical ultrasensitive DNA biosensor to detect Hg2+ based on dark-field microscope and Exo I. Reprinted with permission from [56]. Copyright 2019 Springer Nature.
Biomolecules 11 00399 g004
Figure 5. (a) A scheme of a nicking endonuclease assisted signal amplification for Hg2+ detection based on quantum dots. Reprinted with permission from ref. [65]. Copyright 2013 Elsevier. (b) A scheme of a highly sensitive biosensor for Hg2+ detection based on luminescence resonance energy transfer (LRET) between nanoparticles and SYBR Green I. Reprinted with permission from ref. [66]. Copyright 2019 Elsevier. (c) A scheme of an Hg2+ DNA biosensor based on nickase-assisted signal amplification and DNA assembly. Reprinted with permission from ref. [67]. Copyright 2019 Royal Society of Chemistry (d) A scheme of a sensitive electrochemical biosensor to detect Hg2+ based on nickase Nt.BbvCI and terminal deoxynucleotidyl transferase (TdT). Reprinted with permission from ref. [68]. Copyright 2016 Elsevier.
Figure 5. (a) A scheme of a nicking endonuclease assisted signal amplification for Hg2+ detection based on quantum dots. Reprinted with permission from ref. [65]. Copyright 2013 Elsevier. (b) A scheme of a highly sensitive biosensor for Hg2+ detection based on luminescence resonance energy transfer (LRET) between nanoparticles and SYBR Green I. Reprinted with permission from ref. [66]. Copyright 2019 Elsevier. (c) A scheme of an Hg2+ DNA biosensor based on nickase-assisted signal amplification and DNA assembly. Reprinted with permission from ref. [67]. Copyright 2019 Royal Society of Chemistry (d) A scheme of a sensitive electrochemical biosensor to detect Hg2+ based on nickase Nt.BbvCI and terminal deoxynucleotidyl transferase (TdT). Reprinted with permission from ref. [68]. Copyright 2016 Elsevier.
Biomolecules 11 00399 g005
Figure 6. A scheme of a highly sensitive fluorescence biosensor to test Hg2+ based on DSN and AIE. Reprinted with permission from [69]. Copyright 2017 Springer Nature.
Figure 6. A scheme of a highly sensitive fluorescence biosensor to test Hg2+ based on DSN and AIE. Reprinted with permission from [69]. Copyright 2017 Springer Nature.
Biomolecules 11 00399 g006
Figure 7. (a) A scheme of a nano-graphite-DNA hybrid fluorescent biosensor for Hg2+ detection based on DNase I. Reprinted with permission from [70]. Copyright 2014 Royal Society of Chemistry (b) A scheme of a novel electrochemical biosensor to monitor Hg2+ based on DNase I-assisted target recycling. Reprinted with permission from [73]. Copyright 2016 Elsevier.
Figure 7. (a) A scheme of a nano-graphite-DNA hybrid fluorescent biosensor for Hg2+ detection based on DNase I. Reprinted with permission from [70]. Copyright 2014 Royal Society of Chemistry (b) A scheme of a novel electrochemical biosensor to monitor Hg2+ based on DNase I-assisted target recycling. Reprinted with permission from [73]. Copyright 2016 Elsevier.
Biomolecules 11 00399 g007
Figure 8. The structures and functions of modified DNAzyme for Hg2+ detection. (a) modified UO22+-ion-specific DNAzyme; Reprinted with permission from [18]. Copyright 2007 Wiley VCH. (b) Cu2+-specific DNAzyme; Reprinted with permission from [85]. Copyright 2012 Elsevier. (c) Mg2+-specific DNAzyme. Reprinted with permission from [86]. Copyright 2012 Royal Society of Chemistry.
Figure 8. The structures and functions of modified DNAzyme for Hg2+ detection. (a) modified UO22+-ion-specific DNAzyme; Reprinted with permission from [18]. Copyright 2007 Wiley VCH. (b) Cu2+-specific DNAzyme; Reprinted with permission from [85]. Copyright 2012 Elsevier. (c) Mg2+-specific DNAzyme. Reprinted with permission from [86]. Copyright 2012 Royal Society of Chemistry.
Biomolecules 11 00399 g008
Figure 9. (a) The secondary structure of the originally UO22+-ion-specific DNAzyme, the new DNAzyme with the replaced stem loop, and the stem-loop part of new DNAzymes with 0-6 T-T mismatches. (b) The secondary structure of the Hg2+ biosensor DNAzyme and the scheme of biosensor design. Reprinted with permission from [18]. Copyright 2007 Wiley VCH.
Figure 9. (a) The secondary structure of the originally UO22+-ion-specific DNAzyme, the new DNAzyme with the replaced stem loop, and the stem-loop part of new DNAzymes with 0-6 T-T mismatches. (b) The secondary structure of the Hg2+ biosensor DNAzyme and the scheme of biosensor design. Reprinted with permission from [18]. Copyright 2007 Wiley VCH.
Biomolecules 11 00399 g009
Figure 10. (a) The scheme of DNA biosensor for detecting metal ion including Hg2+ based on the Cu2+-specific DNAzyme and G-quadruplex DNAzymes. (b) The Cu2+-specific DNAzyme, (c) Pb2+-specific DNAzyme, and (d) the modified Cu2+-specific DNAzyme for Hg2+ biosensor. Reprinted with permission from [85]. Copyright 2012 Elsevier.
Figure 10. (a) The scheme of DNA biosensor for detecting metal ion including Hg2+ based on the Cu2+-specific DNAzyme and G-quadruplex DNAzymes. (b) The Cu2+-specific DNAzyme, (c) Pb2+-specific DNAzyme, and (d) the modified Cu2+-specific DNAzyme for Hg2+ biosensor. Reprinted with permission from [85]. Copyright 2012 Elsevier.
Biomolecules 11 00399 g010
Figure 11. (a) The scheme of a fluorescence DNA biosensor to detect Hg2+ based on splitting Mg2+-dependent DNAzyme. Reprinted with permission from [86]. Copyright 2012 Royal Society of Chemistry. (b) The scheme of a visual and sensitive DNA biosensor for Hg2+ detection based on split DNAzyme amplification and peroxidase-like activity of hemin-graphene composites (H-GNs). Reprinted with permission from [92]. Copyright 2019 Elsevier. (c) The scheme of a simple and amplified Hg2+ detection strategy based on DNAzyme motor. Reprinted with permission from [93]. Copyright 2018 Elsevier. (d) The scheme of an electrochemical impedance biosensor for Hg2+ detection based on DNAzyme-assisted target recycling and hybridization chain reaction (HCR). Reprinted with permission from [94]. Copyright 2017 Elsevier.
Figure 11. (a) The scheme of a fluorescence DNA biosensor to detect Hg2+ based on splitting Mg2+-dependent DNAzyme. Reprinted with permission from [86]. Copyright 2012 Royal Society of Chemistry. (b) The scheme of a visual and sensitive DNA biosensor for Hg2+ detection based on split DNAzyme amplification and peroxidase-like activity of hemin-graphene composites (H-GNs). Reprinted with permission from [92]. Copyright 2019 Elsevier. (c) The scheme of a simple and amplified Hg2+ detection strategy based on DNAzyme motor. Reprinted with permission from [93]. Copyright 2018 Elsevier. (d) The scheme of an electrochemical impedance biosensor for Hg2+ detection based on DNAzyme-assisted target recycling and hybridization chain reaction (HCR). Reprinted with permission from [94]. Copyright 2017 Elsevier.
Biomolecules 11 00399 g011
Table 1. The functions of different nucleases mentioned in this review paper.
Table 1. The functions of different nucleases mentioned in this review paper.
TypeNucleaseSubstrateDegradation DirectionReferences
ExonucleaseExo IIIdsDNAForm 3′ to 5′[37,38]
ExonucleaseExo IssDNAForm 3′ to 5′[37,38]
EndonucleaseNickaseOne stand of DNA on dsDNANot Applicable[37]
EndonucleaseDSNdsDNANot Applicable[38]
EndonucleaseDNase IssDNA/dsDNANot Applicable[37]
Table 2. Comparison of biosensors based on different enzymes for mercury detection
Table 2. Comparison of biosensors based on different enzymes for mercury detection
EnzymeDetection LimitLinear RangeIon SpecificityRecovery in Real SamplesReferences
Exo III-one cycle2.3 pM5 pM–10 nMHigh95.7–102%[43]
Exo III-one cycle1 pM1 pM–500 nMHighNot given[26]
Exo III-one cycle3.2 pM10 pM–100 nMHigh92–106%[46]
Exo III-one cycle380 pM1 nM–500 nMHigh97.16–106.61%[47]
Exo III-Two cycles0.9 nM1 nM–10 μMHigh91.2–105.9%[50]
Exo III-Two cycles227 pM500 pM–5 μMHighNot given[51]
Exo III-Two cycles10 fM10 fM–100 nMHigh88–105%[52]
Exo III combination with nanoflowers0.19 fM1 fM–10 nMHigh94.30–106.91%[54]
Exo I15 nMNot givenHighNot given[55]
Exo I combination with microscope36 fM83 fM–8.3 μMHigh96–104%[56]
Nickase0.8 nM1 nM–15 nMHigh93.3–103.8%[65]
Nickase0.14 nM0–2.0 nMHighNot given[66]
Nickase1.7 nM5 nM–250 nMHigh94.2–111.4%[68]
Nickase combination with TdTase3 pM10 pM–100 nMHigh91.5–108.8%[67]
DSN10 fM10 fM to 1 nMHigh97.4–106.8%[69]
DNase I0.5 nM0–200 nMHighNot given[70]
DNase I0.12 nM0.5 nM–50 nMHighNot given[73]
UO22+-specific DNAzyme2.4 nM0–20 nMHighNot given[18]
Cu2+-specific DNAzyme4 nM0–20 nMGood91.3–109.5%[85]
Mg2+-specific DNAzyme0.2 nM1nM–20 nMUltrahigh96–105%[86]
Mg2+-specific DNAzyme33 pM50 pM–1.2 nMGood91.0–108.4%[92]
Mg2+-specific DNAzyme30 pM0.1 nM–5 nMGood94–108%[93]
Mg2+-specific DNAzyme combination with HCR42 fM0.1 pM–10 nMGood95.2–103.3%[94]
Publisher’s Note: MDPI stays neutral with regard to jurisdictional claims in published maps and institutional affiliations.

Share and Cite

MDPI and ACS Style

Wang, S. Construction of DNA Biosensors for Mercury (II) Ion Detection Based on Enzyme-Driven Signal Amplification Strategy. Biomolecules 2021, 11, 399. https://0-doi-org.brum.beds.ac.uk/10.3390/biom11030399

AMA Style

Wang S. Construction of DNA Biosensors for Mercury (II) Ion Detection Based on Enzyme-Driven Signal Amplification Strategy. Biomolecules. 2021; 11(3):399. https://0-doi-org.brum.beds.ac.uk/10.3390/biom11030399

Chicago/Turabian Style

Wang, Shuchang. 2021. "Construction of DNA Biosensors for Mercury (II) Ion Detection Based on Enzyme-Driven Signal Amplification Strategy" Biomolecules 11, no. 3: 399. https://0-doi-org.brum.beds.ac.uk/10.3390/biom11030399

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop