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. 2014 May 23;19(5):6776–6808. doi: 10.3390/molecules19056776

Table 2.

Applications of LPME on sample extracts obtained by conventional solvent extraction.

LPME Analytical techn. Sample Analytes Extraction procedure for solid sample Optimized extraction conditions for s.s. LPME procedure Method performance Ref.
DLLME GC-ECD soil 5 PCBs 1 g s.s. + 10 mL AC; mech. shaking 30 min; upper layer extraction solvent 1.0 mL AC extract (DS) + 30 µL Cl-benzene (ES) inj. into 5.0 mL w.; centrif.; sedim. phase evaporated, rediss. in 20 µL n-hexane η 82.3%–113.6% (3 levels);
RSD < 6.4%;
LOD 0.20–0.50 ng/g
[60]
US-DLLME GC-MS (SIM) soil endosulfan
& 5 metab.
0.5 g s.s. + 1.25 mL AC; US (10 min); centrif. not given AC extract (DS) + 58 μL TCE (ES) inj. into 5.0 mL w. + 7% Na2SO4; US (2 min); centrif.; direct injection experimental design for US-DLLME optimization;
η 89.0%–99.7%; RSD < 6.3%; LOD 0.316–2.494 ng/g;
no interference from sample matrix observed
[61]
DLLME HPLC-FLD sediment PAHs 0.2 g s.s. + 2 mL ACN, VA (2 min), centrif. extraction solvent, vortex time 1.0 mL ACN extract (DS) + 80 μL CH2Cl2 (ES) inj. into 5.0 mL w.; centrif.; sedim. phase evaporated, rediss. in 40 μL ACN η 72.9%–97.8% (3 levels);
RSD < 8.0%; LOD 2.3–6.8 ng/g; no interference from sample matrix observed
[62]
DLLME LC-FLD soil carbaryl, triazophos 1 g s.s. + 10 mL MeOH, mech. shaking (30 min); filtered extraction solvent 1.0 mL MeOH extract (DS) + 50 µL TtCE (ES) inj. into 5.0 mL w.; centrif.; sedim. phase evaporated, rediss. in 25 μL MeOH η 80.8%–111.1% (3 levels);
RSD < 4.3%; LOD 0.014–0.110 ng/g; some matrix interferences present in chromatograms
[63]
US-IL-DLLME HPLC-UV soil 3 pesticides 10 g s.s. + 30 mL sol. (60% MeOH, 5 mg NaCl); US, centrif. + filtr.; repeat; evaporated to dryness, rediss. in 10 mL MeOH sol., pH adjust to 4.0 not given 1.0 mL sample sol., inj. 0.3 mL MeOH (DS) + 70 μL [BMIM]TFSI (ES); shake, US (2 min); centrif.; sedim. phase dissolved in 0.5 mL MeOH not given for overall method (just for DLLME) [64]
IL-DLLME HPLC-FLD soil 5 pesticides
2 metabol.
3 g s.s. + 20 mL MeOH
+ 2.5% NaCl; manual shaking + US; centrif. + filtr.; repeat; evaporated to dryness, rediss. in 10.0 mL w., pH adjust to 5.2
extraction solvent, Vsolv, NaCl add., US time, amount of sample add. NaCl to 30%; MeOH (DS) + IL ([HMIm][PF6], ES);
centrif.; 80 µL sedim. phase dissolved in 1120 µL ACN-phosphate buffer
central composite experimental design for optimization of IL-DLLME conditions;
η 88%–119%;
LOD 0.02–27.1 ng/g
[65]
IL-DLLME HPLC-FLD soil 7 pesticides and metabol. 3 g s.s. + 20 mL MeOH
+ 2.5% NaCl; manual shaking + US (10 min), centrif. + filtr.; repeat; evaporated to dryness, rediss. in 10.0 mL w., pH adjust to 5.2
not given comparison of 2 IL as ES: [PPIm][PF6] and [HMIm][PF6];
add. NaCl (2.5 g); MeOH (DS) 418 μL + IL 117.5 mg (ES); VA 1 min; centrif.; 80 µL sedim. phase dissolved in 1120 µL ACN-phosphate buffer
η 93%–118%; RSD < 20%;
LOD 0.02–60.5 ng/g
[66]
DLLME sweeping
MEKC-DAD
soil 5 sulfonylurea herbicides 10 g s.s. + 10 mL ACN (5% HCOOH, pH 3.0), shaking; added 4 g MgSO4 + 1 g NaCl, shaking; centrif.; 5 mL supernatant + 250 mg C18 + 1.5 g MgSO4, shaking; centrif., filtered extraction solvent, pH of sample solution for DSPE, DSPE sorbent 1.0 mL extract (DS) + 50 µL ClBz inj. into 5.0 mL w. (pH 2.0, HCl), VA (5 s); centrif.; sedim. phase evaporated, rediss. in 20.0 µL phosphate buffer (pH 10.0) η 76.0%–93.5% (3 levels);
RSD < 6.8%;
LOD 0.5–1.0 ng/g
[67]
DLLME HPLC-DAD soil 4 sulfonylurea herbicides 10 g s.s. + 20 mL AC/0.15 M NaHCO3 (2:8), shaking 30 min; filtered; 10 mL filtrate + 0.15 g C18, shaking 5 min; filtered; pH adj. to 2.0 and dil. to 25 mL with AC/w. (2:8, pH 2.0) organic solvent, DSPE sorbent 5.0 mL solution (with AC 20% as DS) + 60 µL ClBz (ES), VA 5 s; centrif.; sedim. phase evaporated, rediss. in 15 µL ACN η 78.0%–92.5% (3 levels);
RSD < 7.2%; LOD 0.5–1.2 ng/g;
some interferences present in chromatograms
[68]
DLLME GC-MS/MS sediment 4 PBDEs 0.25 g s.s. + 1.5 mL AC; US (35 °C) 6 × 5 min; centrif.; 1.2 mL leachate + 100 mg SiO2, VA (30 s); centrif. leaching solvent, Vsolv, DSPE sorbent, US time & mode, US-transmitting liq., leaching T 1.0 mL AC extract (DS) + 60 µL CCl4 (ES) inj. into 5.0 mL w.; shaking, 5 min in bath (35 °C); centrif.; direct injection η 80%–112% (2 levels);
RSD < 9.8%; LOD 0.02–0.06 ng/g;
extraction method comparable efficiency with Soxhlet's
[69]
DLLME GC-MS/MS sediment 4 PBDEs 1 g s.s. + 1.2 mL MeOH; US (40 °C) 2 × 9.2 min; centrif. leaching solvent type (also a DS) & V, T, US time & cycles 0.1 mL MeOH (DS) + 22 mg 1-dodecanol (ES) inj. into 0.4 mL leachate + 1.0 mL 6.15 M NaCl + 4.4 mL w. at 40 °C; SFOD form. at 10 min in ice bath; collected, melt, add. 3 µL i-octane; direct injection factorial (2k) screening & central composite design for optimization; η 71%–104% (2 levels); RSD < 9.2%;
LOD 0.5–1.8 pg/g
[70]
HLLE GC-ECD soil 3 organo-phosph. & pyrethroid pesticides 4.0 g s.s. + 10 mL AC; mech. shaking (30 min); supernatant decanted extraction solvent, Vsolv 1.0 mL AC extract (CS) + 40 µL CCl4 (ES) inj. into 5.0 mL w.; phase separation by 0.3 g NaCl; centrif.; direct injection η 79.2%–113.1%;
RSD < 9.6%;
LOD 0.01–0.04 ng/g
[71]
USA-EME GC-FID soil diazinon, chlorpyrifos 2 g s.s. + 2.5 mL MeOH; US (2 min pulse on/off); centrif., filtered not given 1.5 mL extract + 10.5 mL w.; 14 µL toluene slowly injected during US, US (30 s); centrif.; upper phase collection, direct injection η 90.0%–105%; RSD < 9.2%;
LOD not given for soil; several interferences in the chromatogram
[72]
HF-LPME GC-ICP-MS soil, dust 4 PBDEs 0.5 g soil/0.05 g dust + 3 mL MeOH; US (30 min); centrif.; supernatant diluted to 10 mL with w. not given 3.0 mL extract, 4 µL decane (ES) in 1.5-cm HF; stirring 20 min at 40 °C & 1000 rpm; direct injection η 86.7%–110.9%;
RSD < 10.4%;
LOD not given for soil & dust;
several interferences present in the chromatogram (brominated compounds?)
[73]
HF-LPME GC-ECD sediment vinclozoline 5 g s.s. + 10 mL ACN-MeOH (9:1); US 30 min; centrif., evapor. to 0.05 mL extraction solvent extract + 5 mL w., 3 µL toluene (ES) in 1.3-cm HF; stirring 20 min at 800 rpm; direct injection η 94%–96% (2 levels);
RSD 6.1%;
LOD 0.5 ng/g
[74]
HF-LPME HPLC-FLD soil 7 pesticides and metabol. 3 g s.s. + 20 mL MeOH
+ 2.5% NaCl; manual shaking + US (10 min); centrif. + filtr.; repeat; evaporated to dryness, rediss. in 10.0 mL w., filtered
not given extract (pH adj. to 9.0, NaCl to 20%), 20 µL 1-octanol (ES) in 2.0-cm HF; stirring 30 min at 1440 rpm; ES evaporated, rediss. in 50 µL mobile phase for HPLC η 85%–117%; RSD variable, up to 71% at low levels;
LOD 0.001–6.94 ng/g
[75]
HF-LLLME GC-ECD soil chlorophenols 2 g s.s. + 3 mL MeOH; US (2 min pulse on/off); centrif., filtered not given except for MeOH effect on HF-LLLME 2 mL extract dil. to 20 mL with w., dodecane in 8-cm HF wall (ES) & 25 µL ACN (AS) + IS in HF lumen; stirring 30 min at 400 rpm; direct injection η 86.3%–110%;
RSD < 9.3%;
LOD not given for soil
[58]
HF-LLLME,
dynamic
GC-FID soil PAHs 2 g s.s. + 3 mL MeOH; US (2 min pulse on/off); centrif., filtered not given except for MeOH effect on HF-LLLME 2 mL extract dil. to 20 mL with w. + dodecane in 8-cm HF wall (ES) & 25 µL ACN (AS) in HF lumen; stirring 20 min at 1000 rpm; dynamic extr. (syringe plunger); direct injection η 84.4%–110%;
RSD < 9.3%;
LOD not given for soil
[36]

Abbreviations: ES—extraction solvent; DS—disperser solvent in DLLME; CS—co-solute solvent in HLLE; AS—acceptor solvent in HF-LLLME; HLLE—homogeneous LLE; DSPE—dispersive solid phase extraction; IS—internal standard; s.s.—solid sample. Solvents: AC—acetone; ACN—acetonitrile; ClBz—chlorobenzene; MeOH—methanol; TCE—trichloroethylene; TtCE—tetrachloroethane; w.—water (ultrapure/double deionized/MilliQ); [HMIm][PF6]—1-hexyl-3-methylimidazolium hexafluorophosphate; [PPIm][PF6]—1,3-dipentylimidazolium hexafluorophosphate.