Table 3.
Representative studies of colorimetric analysis of heavy metals from food and water resources based on nanoparticle aggregation.
Electrode | Sample | Linear Range | Limits of Detection | Ref. |
---|---|---|---|---|
MPBA/AuNPs | Water samples | 0.01–5 μM Hg2+ | 8 nM Hg2+ | [61] |
(en)/S2O32−/AuNPs | Drinking water | 0.1–0.7 μM Co2+ | 0.04 μM (2.36 ppb) Co2+ | [62] |
4-MB/AuNPs (S2O32−) | River water, Montana soil, and urine samples | 0.5–10 nM Pb2+ | 0.2 nM Pb2+ | [63] |
Tween 20/Citrate ions/AuNPs | Drinking water and seawater sample |
/ | 0.1 μM Hg2+; Ag+ | [64] |
DTETAuNPs | Water sample | 1–6 μM Hg2+ | 100 nM Hg2+ | [67] |
AuNPs/g-CQDs | Mice organ tissues sample | 0.01–3.0 μM Cd2+ | 10 nM Cd2+ | [69] |
AuNPs/GO/S2O32− | Pure drinking water and river water samples | 0.1–20 μM Pb2+ | 0.05 μM Pb2+ | [70] |
TMA/AgNPs | Tap, lake, and river water sample | / | 0.5 nM Cu2+ | [71] |
SAA/AgNPs | Tap water, lake water, milk, urine, and serum sample | 0.05–1.1 μM Cd2+ | 3.0 nM Cd2+ | [72] |
AgNPs/biopolymer xylan | River water samples | 10–500 μM Hg2+ | 4.6 nM Hg2+ | [73] |
PAA/AgNCs | Tap water and mineral water samples | 0–20 μM Hg2+ | 2 nM Hg2+ | [74] |
Carr/Ag/AgCl NPs | Environmental or biological samples | 1–100 μM Hg2+ | 1 μM Hg2+ | [75] |
AgNPs | Metal ions sample | 3–30 nM Hg2+ | 0.037 nM Hg2+ | [76] |
Abbreviations: 4-mercaptophenylboronic acid (MPBA), Au nanoparticles (AuNPs), ethylenediamine (en), thiosulfate (S2O32−), 4-mercaptobutanol (4-MB), dithioerythritol-modified AuNPs (DTET-AuNPs), graphite-like nitride doped carbon quantum dots (g-CQDs), graphene oxide (GO), thiomalic acid functionalized silver nanoparticles (TMA/AgNPs), sulfosalicylic acid functionalized silver nanoparticles (SAA/AgNPs), poly(acrylic acid)-templated silver nanoclusters (PAA/AgNCs), carrageenan (Carr), Ag nanoparticles (AgNPs).