Skip to main content
. 2009 Jan 9;14(1):298–320. doi: 10.3390/molecules14010298

Table 3.

Methods for the determination of phenolic compounds using surfactant solutions.

Matrix Extraction technique Surfactants Recoveries (%) LOD Instrumental Analysis Ref.
Sea water waste water CPE Oligoethylene glycol monoalkyl ether (Genapol X-080) 66-119 1.0-5.0 (µg.L-1) LC-UV [83]
Sea water waste water CPE Polyoxyethylene 10 lauryl ether (POLE) Polyoxyethylene 9 lauryl ether (Polidocanol) Polyoxyethylene 6 lauryl ether (C12E6) 44-115 0.6–3.5 (µg.L-1) LC-UV [84]
Water CPE Poly(oxyethylene)-7,5-( p-tert-octylphenyl) ether (Triton X-114) 62-101 2.0-5.0 (µg.L-1) LC-UV-EC [85]
River water lake water CPE Triton X-114 93-103 2.0-2.5 (mol.L−1) CE-UV [95]
Sediments MAME Polyoxyethylene-6-lauryl ether 81-120 1.2–12.7(µg.g−1) LC-UV [87]
Soil MAME POLE 70-118 LC-UV [88]
Sediments MAME (Polidocanol) Oligoethylene glycol monoalkyl ether (Genapol X-080) 79-117 2-20 (µg.g-1) LC-UV [94]
Sea water, sewage water ground water SPME-MD CW-TPR POLE 89-107 1.1-5.9 (µg.L-1) LC-UV [86]
Sea water, sewage water ground water SPME-MD CW-TPR PDMS PDMS-DVB PA Carboxen-PDMS POLE, Polidocanol, Polyoxyethylene 6 lauryl ether (C12E6) Hexadecyltrimethylammonium bromide (HTAB) 80-109 0.3–3.5(µg.L-1) LC-UV [50]
Wood MAME-MSPME PA POLE 71-125 0.002-0.12 (µg.g-1) GC-MS [90]