Table 1.
Atomic spectrophotometric and UV–Vis spectrophotometric techniques coupled with hollow fiber based extraction techniques for heavy metals determination.
| Instrumental techniques | Metal/Analyte | Preconcentratio/Separation method | Complexing agent/Carrier | SLM composition | Real applications | LODa | EF/PFb | LRc | Instrumental technique mode | Ref. |
|---|---|---|---|---|---|---|---|---|---|---|
| Atomic spectroscopic techniques | Pb | HFSLPME | TiO2 | TiO2 + Caprylic acid | Rice, milk, water | 0.2 μg/L | 790 | 0.6–3000 μg/mL | FAAS | [51] |
| As | HFLPME | APDC | Triton X-100 | Environmental water samples | 0.08 ng/mL | 280 | 0.4–12 ng/mL | FAAS | [52] | |
| Cr (VI) | IEME | — | 1-octanol | Environmental water samples | 3 ng/mL | 23 | 10–600 ng/mL | FAAS | [53] | |
| Pb | HFLPME | Kronenether | Kronenether + oleic acid | Blood, urine samples | 0.001–0.002 ng/mL | 18.7–21.3 | 1–50 ng/mL | GFAAS | [54] | |
| Hg | EME | DEHP | DEHP + 1-octanol | Tap water | 0.5 μg/L | 102–108 | 0.5–10 μg/L | GFAAS | [55] | |
| Cr(VI) | EME | PANI | PANI + 1-octanol | Spring, sea and distilled water | 0.02 ng/mL | 106 | 0.02–2.0 ng/mL | ETAAS | [56] | |
| Cr(VI) | HFLPME | Methyltrialkylammonium chloride | Methyltrialkylammonium chloride + 1-octanol | Drinking, mineral and tap water | 3 μg/L | — | 10–90 μg/L | RGB/ ICP-AES | [57] | |
| Pb | CM-HFLPME | CTAB | CTAB + 1-octanol | Blood samples | 0.1 ng/mL | 33 | 1–200 ng/mL | ETAAS | [58] | |
| Cr (VI) | μEME | Tetra alkyl ammonium chloride | Tetra alkyl ammonium chloride+ 1-octanol | Wastewater samples | 0.06 ng/mL | 9.1 | 0.5–14 ng/mL | ETAAS | [59] | |
| Hg | HFLPME | DDTC | DDTC + toluene | Water and freshwater fish | 0.143 | 103 | 0.5–7.5 | ETAAS | [60] | |
| UV–visible spectrometry | Cr (VI) | EME | 1,5-diphenylcarbazide | NPOE | Environmental water samples | 2.3–7 μg/L | 80 | 10–80 μg/L | UV–vis spectrometry | [61] |
| Cr (VI) | EME | Calix[4]arene | NPOE + calix[4]arene | Industrial water | — | — | — | UV–vis spectrometry | [62] | |
| Hg | EME | DEHP | 1-octanol | River, tap water and fish sample | 0.7–12 μg/kg | 130–176 | 2.3–950 μg/L for water and 40–9500 μg/kg for fish sample | UV–vis spectrometry | [63] | |
| Au | EME | PAN | 1-octanol | Tap, river and ground water | 4.5 μg/L | 200 | 20–2000 μg/L | UV–vis spectrometry | [64] | |
| Bi +3 | EME | DEHP | DEHP + 1-octanol | Plasma, water | 1.47 μg/L | 151 | 4.9–800 μg/L | UV–vis spectrometry | [65] |
EME: Electro-membrane extraction, HFLPME: Hollow fiber liquid phase microextraction, IEME: In-tube electro-membrane extraction, CM-HFLPME: carrier-mediated hollow fiber liquid phase microextraction, DEHP: bis(2-ethylhexyl) phosphate, CTAB: N,N,N-cetyltrimethyl ammonium bromide, APDC: Ammonium pyrroldinedithiocarbamate, PANI: Polyanniline, DDTC: Diethyldithiocarbamate, PAN: 1-(2-pyridylazo)-2-naphthol), NPOE: 2-nitrophenyl octyl ether, FAAS: Flame atomic absorption spectroscopy, GFAAS: Graphite furnace atomic absorption spectrometry, ETV-ICP-OES: Electrothermal vaporization inductive couple plasma optical emission spectroscopy, RGB/ ICP-AES: Red Green Blue Analysis/ inductive couple plasma atomic emission spectroscopy.
Limit of detection.
Enrichment factor/Pre-concentration factor.
Linear range.