Table 2.
S. number | Analyte | Analytical instrument used for the detection | Method | Limit of detection (LOD)# | Linearity range | Analyzed samples | Interference study | Supporting media | Reference |
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1 | Hg(II) | Fluorescence spectrophotometer | Fluorescence | 4.0 × 10−9 M | 6.0–450 nM | Water samples | 10-fold of Pb2+, Cu2+, and Ag+ shows <7% influence on the determination of Hg2+ compared to reported ones | CdTe quantum dots | [80] |
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2 | Hg(II) | Spectrophotometer | Colorimetric | 23 × 10−9 M | 0.00–0.31 μM | River water | Selective in presence of Ag+, Cd2+, Cu2+, Co2+, Ni2+, and Pb2+ | Carbon nanodots | [81] |
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3 | Hg(II) | Spectrophotometer | Colorimetric | 2.6 × 10−9 M | 0.001–1 μM | Water samples | Selective in presence of 20 μM of Al3+, Ca2+, Co2+, Cu2+, Cd2+, Fe3+, Mn2+, Ni2+, Pb2+, and Zn2+ | Gold nanoparticles | [82] |
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4 | Hg(II) | Spectrophotometer | Colorimetric | — | 0.83–8.6 μg mL−1 | Water samples | The tolerance limit of Cu2+, V5+, Ag+, Pd2+, Pt4+, Au3+, Fe2+, Ni2+, Cd2+, Pb2+, and Cr6+ is in the range of 0.11–041 μg mL−1in the determination of 1.91 μg mL−1 of Hg2+ | 5-Methylthiophene-2-carboxaldehyde ethylenediamine | [83] |
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5 | Hg(II) | Spectrofluorometer | Fluorescence | 1.73 × 10−9 M | 2.0 nM–60 μM | — | Interference of major cations studied | ONPCRs1 | [84] |
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6 | Hg(II) | Spectrophotometer | Colorimetric | 50 × 10−9 M2 | 0–1000 nM | Water samplers | Selective in presence of Ni2+, Co2+, Ca2+, Cu2+, Na+, K+, As3+, Mg2+, Cd2+, and Fe2+ | Silver nanoparticles | [85] |
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7 | Hg(II) | UV-Vis spectrophotometer | Colorimetric | 1.35 × 10−6 M | — | Drinking water | Cd2+, Pb2+, Fe3+, and Ba2+ do not interfere in the determination of Hg2+ but Mg2+, Ca2+, and Mn2+ interfere slightly | Gold nanoparticles | [86] |
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8 | Hg(II) | Spectrofluorometer and UV-spectrometer | Colorimetric and fluorescent sensor | 2.7 × 10−8 M | 0–1.0 × 10−6 M | Water samples and living cells | The fluorescent signal for Hg(II) is not influenced by the major metal ions including Fe(III), Cu(II), and Al(III) | 2,4-Dichloroquinazoline | [87] |
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9 | Hg(II) | Spectrophotometer | Colorimetric | 5.3 × 10−13 M | 1.0 × 10−12–8.6 × 10−4 M | Water samples and SRM | Selective in presence of Mn2+, Fe2+, Fe3+, Ni2+, Co2+, Cd2+, and Pb2+ | Chromoionophore V | [88] |
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10 | Hg(II) | Spectrofluorometer | Fluorescent and colorimetric | 1.0 × 10−9 M | — | Spiked water samples | Na+, Mg2+, K+, Cr3+, Mn2+, Co2+, Ni2+, Fe3+, Cu2+, Zn2+, Ag+, Cd2+, and Pb2+ did not interfere | Rhodamine B | [89] |
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11 | Hg(II) | Spectrofluorometer | Fluorescence | 14.2 × 10−9 M | 0–5 × 10−7 M | Aqueous solutions | Cd2+, Cu2+, and Ag+ do not interfere | Thioether-appended dipeptide | [90] |
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12 | Hg(II) | Spectrofluorometer | Fluorescence | 0.5 × 10−9 M | 0.0005–0.01 μM | Lake water samples | Zn2+, Pb2+, Ni2+, Ca2+, Mg2+, Cu2+, Co2+, Cd2+, Fe3+, and Mn2+ did not interfere | Carbon nanotubes | [91] |
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13 | Hg(II) | Spectrofluorometer | Fluorescent | 1.74–3.83 × 10−6 M | — | Living cells | Minor interference from Ag+, Ca2+, Cd2+, Co2+, Cu2+, Fe2+, Fe3+, K+, Mg2+, Mn2+, Na+, Ni2+, Pb2+, Rb+, and Zn2+ | Pyrene | [92] |
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14 | Hg(II) | Spectrophotometer | Colorimetric | 0.4 × 10−6 M | 0.1–4.2 μg mL−1 | Water, biological, plant leaves, and soil samples | Tolerance limit of the Cd2+, Zn2+, Ce3+, Ce4+, In3+, Cr3+, La3+, Yb3+, and Eu3+ is 300 μg mL−1 and the tolerance limit of the Co2+, Cu2+, Fe3+, Ti4+, Pb2+, Ni2+, and Ag+ is 100 μg mL−1 and at Hg(II) is 2.0 μg mL−1 | 2,4,7-Triamino-6-phenylpteridine | [93] |
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15 | Hg(II) | Spectrofluorophotometer | Fluorescent | 1.0 × 10−7 M | 2.0 × 10−7–3.0 × 10−5 M | Water samples | Selective in presence of Na+, K+, NH4 +, Ba2+, Zn2+, Cd2+, Mg2+, Ca2+, and Ni2+ | Conjugated polymer multilayer films | [94] |
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16 | Hg(II) | Spectrophotometer | TGFRET3 | 0.49–0.87 × 10−9 M | 1.0 × 10−9–1.0 × 10−8 M | Water samples | Selective in presence of Mn2+, Ba2+, Ni2+, Cu2+, Ca2+, Cr2+, Co2+, Cd2+, Mg2+, Zn2+, Al3+, Fe3+, and Pb2+ | Gold nanoparticles | [95] |
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17 | Hg(II) | Spectrofluorometer | Fluorescent | 1 × 10−9 M | 0.01–0.12 μM | Water samples | Selective in presence of Zn2+, Pb2+, Ni2+, Co2+, Ca2+, Cu2+, Mg2+, Cd2+, Fe3+, and Mn2+ | Carbon nanodots | [96] |
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18 | Hg(II) | Spectrofluorometer | Fluorescent | 0.012 × 10−6 M | 0-1 μM | Tap and river water samples | Selective in presence of Ag+, Pb2+, Na+, K+, Cr3+, Cd2+, Ba2+, Zn2+, Mg2+, Cu2+, Ni2+, Ca2+, Al3+, and Fe3+ | Rhodamine | [97] |
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19 | Hg(II) | Spectrofluorometer | Fluorescence | 2.24 × 10−9 M | 5.0–100 nM | Drinking water | 20-fold of Ca2+, Mg2+, Zn2+, Cr3+, Pb2+, Cr6+, Mn2+, Cd2+, Fe3+, Al3+, and Ni2+, 10-fold of Fe2+, and Co2+, 5-fold of Cu2+, and the same concentration of Ag+ caused almost no interference | Gold nanoparticles | [98] |
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20 | Hg(II) | Spectrophotometer | Optical chemical sensor | 0.18 × 10−12 M | 7.2 × 10−13–4.7 × 10−4 M | Tap water, river water, and canned tuna fish | Interference of Cu(II) eliminated with the addition of L-histidine as a masking agent | Synthesized ionophore | [99] |
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21 | Hg(II) | UV-Vis spectrophotometer | Colorimetric sensor | 5.0 × 10−6 M (visual), 1.0 × 10−7 M (UV-Vis) | — | Aqueous solutions | Mg2+, Ca2+, Zn2+, Cu2+, Cr3+, Fe3+, Pb2+, Ni2+, Co2+, and Ag+ did not interfere | Dimethyl sulphoxide | [100] |
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22 | Hg(II) | Fluorescence spectrophotometer | Fluorescence probe | 16 × 10−9 M | 0.02–1.0 μM | Aqueous solutions | Selective in the determination of Hg2+ over other metal ions such as Fe3+, Ca2+, Mg2+, Mn2+, Cr3+, Ni2+, Cu2+, Co2+, and Pb2+ | Gold nanoparticles | [101] |
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23 | Hg(II) | — | Colorimetric | 1.2 × 10−9 M | 2–30 nM | Water samples | Na+ (2 mM), K+ (2 mM), Fe3+, Zn2+ and Mg2+ (0.1 mM), Ni2+, Co2+, Cd2+, Pb2+ and Cu2+ (50 μM), and Ag+ (3.5 μM) did not interfere with the detection of Hg2+ (25 nM) in the mentioned amounts | Rhodamine B thiolactone | [102] |
#For the conversion of limit of detection values into moles per liter (M) the atomic weight of Hg is taken as 200.59 g, MeHg as 215.59 g, EtHg as 229.59 g, and PhHg as 277.59 g.
1ONPCRs: oxygen-doped nitrogen-rich photoluminescent polymer carbon nanoribbons; 2Limit of quantification; 3TGFRET: time-gated fluorescence resonance energy transfer.