Chinese Journal of Chromatography ›› 2021, Vol. 39 ›› Issue (8): 781-801.DOI: 10.3724/SP.J.1123.2021.02030
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FENG Juanjuan, JI Xiangping, LI Chunying, SUN Mingxia, HAN Sen, FENG Jiaqing, SUN Haili, FENG Yang, SUN Min*()
Received:
2021-02-28
Online:
2021-08-08
Published:
2021-06-29
Contact:
SUN Min
Supported by:
CLC Number:
FENG Juanjuan, JI Xiangping, LI Chunying, SUN Mingxia, HAN Sen, FENG Jiaqing, SUN Haili, FENG Yang, SUN Min. Recent advance of new sample preparation materials in the analysis and detection of environmental pollutants[J]. Chinese Journal of Chromatography, 2021, 39(8): 781-801.
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URL: https://www.chrom-china.com/EN/10.3724/SP.J.1123.2021.02030
Adsorbent | Analytes | Sample | LODs/(μg/L) | Linear range/(μg/L) | Analytical method | |||
---|---|---|---|---|---|---|---|---|
GO-PDAP[ | Cd2+ | water | 0.47 | 2 | -100 | SPE-FAAS | ||
GO/polyaniline[ | Cd2+ | water | 0.1 | 0.4 | -1000 | SPE-DLLME-FAAS | ||
Al2O3/GO[ | Cr3+, As5+ | water | 0.11 | , 0.02 | 2.0 | -50 | D-μ-SPE-EDXRF | |
POT/GO[ | three nonsteroidal anti- inflammatory drugs | water | 0.02 | -0.03 | 0.08 | -200 | D-μ-SPE-HPLC-UV | |
GO@NH2@Fe3 | twelve quinolones | water | 10.0 | - | MSPE-MALDI-TOF MS | |||
M-MOF-199[ | five triazole pesticides | water | 0.05 | -0.1 | 0.25 | -1000 | MSPE-HPLC-MS/MS | |
Fe3O4@HP-β-CD-RGO[ | Cd2+ | water | 0.23 | 0.50 | -100.0 | MSPE-FAAS | ||
MG/PDA[ | four benzoylurea insec- ticides | water | 0.75 | 2.5 | -500 | MDSPE-HPLC-DAD | ||
MG/CNTs/PDA[ | sixteen PAHs | water | 0.0001 | -0.003 | 0.010 | -0.500 | MSPE-GC-MS | |
MGO@mSiO2-MIPs[ | six PAEs | water | 0.01 | -0.05 | 1 | -50 | MSPE-GC-MS | |
GO@Fe3O4-MIP[ | microsystin-LR | water | 0.08 | 2 | -10000 | MSPE-HPLC-UV | ||
G[ | six PAHs | water | 0.01 | -0.09 | 0.05 | -50 | HS-SPME-GC-FID | |
3D-rGO-PANI[ | ethion | water | 0.4 | 1.0 | -70 | DI-SPME-HPLC | ||
GO[ | five PAHs | water | 0.05 | -0.10 | 0.5 | -200 | SPME-GC | |
G[ | five n-alkanes | water | 0.05 | -0.50 | 0.2 | -150 | SPME-GC | |
GO reinforced PILs monolith[ | phenols | water | 0.20 | -0.50 | 5 | -400 | SPME-HPLC | |
GO-CFs[ | ten PAHs | wastewater | 0.001 | -0.004 | 0.003 | -50 | IT-SPME-HPLC-DAD |
Table 1 Recent applications of graphene (G) and graphene oxide (GO)-based adsorbents for sample preparation in analysis and detection of environmental pollutants
Adsorbent | Analytes | Sample | LODs/(μg/L) | Linear range/(μg/L) | Analytical method | |||
---|---|---|---|---|---|---|---|---|
GO-PDAP[ | Cd2+ | water | 0.47 | 2 | -100 | SPE-FAAS | ||
GO/polyaniline[ | Cd2+ | water | 0.1 | 0.4 | -1000 | SPE-DLLME-FAAS | ||
Al2O3/GO[ | Cr3+, As5+ | water | 0.11 | , 0.02 | 2.0 | -50 | D-μ-SPE-EDXRF | |
POT/GO[ | three nonsteroidal anti- inflammatory drugs | water | 0.02 | -0.03 | 0.08 | -200 | D-μ-SPE-HPLC-UV | |
GO@NH2@Fe3 | twelve quinolones | water | 10.0 | - | MSPE-MALDI-TOF MS | |||
M-MOF-199[ | five triazole pesticides | water | 0.05 | -0.1 | 0.25 | -1000 | MSPE-HPLC-MS/MS | |
Fe3O4@HP-β-CD-RGO[ | Cd2+ | water | 0.23 | 0.50 | -100.0 | MSPE-FAAS | ||
MG/PDA[ | four benzoylurea insec- ticides | water | 0.75 | 2.5 | -500 | MDSPE-HPLC-DAD | ||
MG/CNTs/PDA[ | sixteen PAHs | water | 0.0001 | -0.003 | 0.010 | -0.500 | MSPE-GC-MS | |
MGO@mSiO2-MIPs[ | six PAEs | water | 0.01 | -0.05 | 1 | -50 | MSPE-GC-MS | |
GO@Fe3O4-MIP[ | microsystin-LR | water | 0.08 | 2 | -10000 | MSPE-HPLC-UV | ||
G[ | six PAHs | water | 0.01 | -0.09 | 0.05 | -50 | HS-SPME-GC-FID | |
3D-rGO-PANI[ | ethion | water | 0.4 | 1.0 | -70 | DI-SPME-HPLC | ||
GO[ | five PAHs | water | 0.05 | -0.10 | 0.5 | -200 | SPME-GC | |
G[ | five n-alkanes | water | 0.05 | -0.50 | 0.2 | -150 | SPME-GC | |
GO reinforced PILs monolith[ | phenols | water | 0.20 | -0.50 | 5 | -400 | SPME-HPLC | |
GO-CFs[ | ten PAHs | wastewater | 0.001 | -0.004 | 0.003 | -50 | IT-SPME-HPLC-DAD |
Adsorbent | Analytes | Sample | LOD | Linear range | Analytical method |
---|---|---|---|---|---|
MWCNTs[ | atrazine | water | 0.66 μg/L | 2-100 μg/L | SPE-BCAE-HPLC-UV |
HCl-treated MWCNTs[ | thirteen pharmaceuticals and two metabolites of metamizole | water | 0.2-103 ng/L | 10-250 μg/L | SPE-HPLC-MS/MS |
ox-MWCNTs[ | three progestins | water | 0.05-0.14 μg/L | 0.90-9.0 μg/L | SPE-HPLC-UV |
3D MWCNTs@g-C3N4@ Fe3 | sixteen PAHs | water | 0.001-0.5 μg/L | 0.2-200 μg/L | MSPE-GC-FID |
M-M-ZIF-67[ | nine organochlorine pesticides | agricultural water | 0.07-1.03 μg/L | 1-200 μg/L | MSPE-GC-MS/MS |
MMP/ZIF-8[ | five triazole fungicides | water | 0.08-0.27 μg/L | 1-400 μg/L | MSPE-GC-MS/MS |
MFCA[ | nine perfluorocarboxylic acids and perfluorosulfonic acids | water | 0.010-0.50 ng/L | 0.4-10000 ng/L | MSPE-HPLC-MS/MS |
oxidized MWCNTs[ | four PAHs | water | 2-20 ng/L | 10-500 ng/L | HS-SPME-GC-MS |
oxidized-CNTs[ | menthol | water | 20 μg/L | 50-100000 μg/L | HS-SPME-GC-FID |
MWCNTs/NaDC[ | five phenols | seawater | 0.15-0.30 μg/L | 1-100 μg/L | SPME-HPLC-UV |
CNT/magnetite/PA[ | four phenols | water | 0.008-0.07 μg/L | 0.01-500 μg/L | SPME-GC-MS |
MNC[ | glucocorticoid | water | 0.0075-0.16 ng/L | 0.05-1000 ng/L | MSPE-HPLC-MS/MS |
CNT-Ti | seven PAHs | water | 0.002-0.004 μg/L | 0.01-200 μg/L | SPME-GC |
Table 2 Recent applications of carbon nanotubes-based adsorbents for sample preparation in analysis and detection of environmental pollutants
Adsorbent | Analytes | Sample | LOD | Linear range | Analytical method |
---|---|---|---|---|---|
MWCNTs[ | atrazine | water | 0.66 μg/L | 2-100 μg/L | SPE-BCAE-HPLC-UV |
HCl-treated MWCNTs[ | thirteen pharmaceuticals and two metabolites of metamizole | water | 0.2-103 ng/L | 10-250 μg/L | SPE-HPLC-MS/MS |
ox-MWCNTs[ | three progestins | water | 0.05-0.14 μg/L | 0.90-9.0 μg/L | SPE-HPLC-UV |
3D MWCNTs@g-C3N4@ Fe3 | sixteen PAHs | water | 0.001-0.5 μg/L | 0.2-200 μg/L | MSPE-GC-FID |
M-M-ZIF-67[ | nine organochlorine pesticides | agricultural water | 0.07-1.03 μg/L | 1-200 μg/L | MSPE-GC-MS/MS |
MMP/ZIF-8[ | five triazole fungicides | water | 0.08-0.27 μg/L | 1-400 μg/L | MSPE-GC-MS/MS |
MFCA[ | nine perfluorocarboxylic acids and perfluorosulfonic acids | water | 0.010-0.50 ng/L | 0.4-10000 ng/L | MSPE-HPLC-MS/MS |
oxidized MWCNTs[ | four PAHs | water | 2-20 ng/L | 10-500 ng/L | HS-SPME-GC-MS |
oxidized-CNTs[ | menthol | water | 20 μg/L | 50-100000 μg/L | HS-SPME-GC-FID |
MWCNTs/NaDC[ | five phenols | seawater | 0.15-0.30 μg/L | 1-100 μg/L | SPME-HPLC-UV |
CNT/magnetite/PA[ | four phenols | water | 0.008-0.07 μg/L | 0.01-500 μg/L | SPME-GC-MS |
MNC[ | glucocorticoid | water | 0.0075-0.16 ng/L | 0.05-1000 ng/L | MSPE-HPLC-MS/MS |
CNT-Ti | seven PAHs | water | 0.002-0.004 μg/L | 0.01-200 μg/L | SPME-GC |
Adsorbents | Analytes | Samples | LODs | Linear ranges | Analytical methods |
---|---|---|---|---|---|
CA[ | ten HD | environmental pore water | 0.17-0.50 μmol/L | 1.0-20 μmol/L | SPE-HPLC-DAD |
Biocharcoal aerogel[ | eight PAHs | water, honey and pear syrup | 0.005-0.050 μg/L | 0.017-15 μg/L | IT-SPME-HPLC-DAD |
CA[ | six organophosphorus pesticides | environmental water | 0.09 μg/L | - | liquid-phase microextraction-SESI-IMS |
CA[ | six organophosphorus pesticides | environmental water | 0.11-0.83 μg/L | - | SPME-GC-MS |
IL-CA[ | tetracyclines | water | 0.36-0.71 μg/L | 2-1000 μg/L | SPME-HPLC-UV |
GA[ | three endocrine disrupting chemicals and seven polychlorinated biphenyls | river, lake, drinking and tap water | 0.01-0.11 μg/L, 0.19-1.53 ng/L | 0.05-100 μg/L, 0.01-5 μg/L | SPE-HPLC and SPE-GC-MS |
GA[ | five pyrethroids | drinking water | 0.83-9.31 ng/L | 0.02-10 μg/L | SPE-GC-MS |
GA[ | six organophosphorus pesticides | river water | 0.12-0.58 μg/L | 0.5-500 μg/L | SPE-GC-MS |
GA[ | six chlorophenols | soil | 0.02-0.10 μg/L | 50-1000 μg/L | MSPD-HPLC-UV |
GA[ | eight phenols | river water | 0.016-0.075 μg/L | 0.05-40 μg/L | in-syringe SPE-HPLC-UV |
GA[ | six pyrethroids | river water | 0.012-0.11 μg/L | 0.2-50 μg/L | in-syringe SPE-GC-MS |
GCA[ | eight PAHs | river, tap water | 1.7-8.8 ng/L | 10-2000 ng/L | SPE-GC-MS |
C-MWCNT-GA[ | six organophosphorus pesticides | wetland, lake, and river water | 0.28-0.52 μg/L | 0.96-1.64 μg/L | SPE-GC-MS |
Silica aerogel[ | eight PAHs | bottled water, tap water, river water and tea water | 0.005-0.050 μg/L | 0.017-15 μg/L | IT-SPME-HPLC-DAD |
Trimethylchlorosilane modified nanoporous silica aerogel[ | four chlorobenzenes | water | 0.4-0.8 ng/L | 3-3000 ng/L | headspace needle trap extraction-GC-MS |
Triethylchlorosilane modified nanoporous silica aerogel[ | four chlorobenzenes | water | 0.3-1 ng/L | 3-3000 ng/L | headspace needle trap extraction-GC-MS |
Organic-inorganic hybrid silica aerogel[ | eight PAHs | water | 0.001-0.030 μg/L | 0.005-20 μg/L | fiber SPME-GC-FID |
Organically modified silica aerogel[ | five estrogens | sewage and emollient water | 0.01-0.05 μg/L | 0.03-100 μg/L | IT-SPME-HPLC-DAD |
Table 3 Recent applications of inorganic aerogels for sample preparation in analysis and detection of environmental pollutants
Adsorbents | Analytes | Samples | LODs | Linear ranges | Analytical methods |
---|---|---|---|---|---|
CA[ | ten HD | environmental pore water | 0.17-0.50 μmol/L | 1.0-20 μmol/L | SPE-HPLC-DAD |
Biocharcoal aerogel[ | eight PAHs | water, honey and pear syrup | 0.005-0.050 μg/L | 0.017-15 μg/L | IT-SPME-HPLC-DAD |
CA[ | six organophosphorus pesticides | environmental water | 0.09 μg/L | - | liquid-phase microextraction-SESI-IMS |
CA[ | six organophosphorus pesticides | environmental water | 0.11-0.83 μg/L | - | SPME-GC-MS |
IL-CA[ | tetracyclines | water | 0.36-0.71 μg/L | 2-1000 μg/L | SPME-HPLC-UV |
GA[ | three endocrine disrupting chemicals and seven polychlorinated biphenyls | river, lake, drinking and tap water | 0.01-0.11 μg/L, 0.19-1.53 ng/L | 0.05-100 μg/L, 0.01-5 μg/L | SPE-HPLC and SPE-GC-MS |
GA[ | five pyrethroids | drinking water | 0.83-9.31 ng/L | 0.02-10 μg/L | SPE-GC-MS |
GA[ | six organophosphorus pesticides | river water | 0.12-0.58 μg/L | 0.5-500 μg/L | SPE-GC-MS |
GA[ | six chlorophenols | soil | 0.02-0.10 μg/L | 50-1000 μg/L | MSPD-HPLC-UV |
GA[ | eight phenols | river water | 0.016-0.075 μg/L | 0.05-40 μg/L | in-syringe SPE-HPLC-UV |
GA[ | six pyrethroids | river water | 0.012-0.11 μg/L | 0.2-50 μg/L | in-syringe SPE-GC-MS |
GCA[ | eight PAHs | river, tap water | 1.7-8.8 ng/L | 10-2000 ng/L | SPE-GC-MS |
C-MWCNT-GA[ | six organophosphorus pesticides | wetland, lake, and river water | 0.28-0.52 μg/L | 0.96-1.64 μg/L | SPE-GC-MS |
Silica aerogel[ | eight PAHs | bottled water, tap water, river water and tea water | 0.005-0.050 μg/L | 0.017-15 μg/L | IT-SPME-HPLC-DAD |
Trimethylchlorosilane modified nanoporous silica aerogel[ | four chlorobenzenes | water | 0.4-0.8 ng/L | 3-3000 ng/L | headspace needle trap extraction-GC-MS |
Triethylchlorosilane modified nanoporous silica aerogel[ | four chlorobenzenes | water | 0.3-1 ng/L | 3-3000 ng/L | headspace needle trap extraction-GC-MS |
Organic-inorganic hybrid silica aerogel[ | eight PAHs | water | 0.001-0.030 μg/L | 0.005-20 μg/L | fiber SPME-GC-FID |
Organically modified silica aerogel[ | five estrogens | sewage and emollient water | 0.01-0.05 μg/L | 0.03-100 μg/L | IT-SPME-HPLC-DAD |
Adsorbent | Analytes | Samples | LOD/(μg/L) | Linear range/(μg/L) | Analytical method |
---|---|---|---|---|---|
MF aerogel[ | eight PAHs | rain and tap water | 0.01-0.05 | 0.06-30 | IT-SPME-HPLC-DAD |
BNNs/MF aerogel[ | eight PAHs | rain and soil solution | 0.005-0.010 | 0.016-20 | IT-SPME-HPLC-DAD |
PDA-MF aerogel[ | seven PAEs | surface water | 0.02-0.05 | 0.07-30 | IT-SPME-HPLC-DAD |
IL modified MF aerogel[ | five estrogens | water, aloe | 0.05-0.20 | 0.15-20 | IT-SPME-HPLC-DAD |
RF aerogel[ | five estrogens | water | 0.005-0.030 | 0.017-20 | IT-SPME-HPLC-DAD |
Al(Ⅲ)-MOA[ | BTEX, five phenols | water | - | - | HS-SPME-GC-MS |
MOA[ | five chlorobenzenes | river and tap water, | 0.0001-0.06 | 0.0004-20 | HS-SPME-GC-ECD |
sludge and coastal soil |
Table 4 Recent applications of organic aerogels for sample preparation in analysis and detection of environmental pollutants
Adsorbent | Analytes | Samples | LOD/(μg/L) | Linear range/(μg/L) | Analytical method |
---|---|---|---|---|---|
MF aerogel[ | eight PAHs | rain and tap water | 0.01-0.05 | 0.06-30 | IT-SPME-HPLC-DAD |
BNNs/MF aerogel[ | eight PAHs | rain and soil solution | 0.005-0.010 | 0.016-20 | IT-SPME-HPLC-DAD |
PDA-MF aerogel[ | seven PAEs | surface water | 0.02-0.05 | 0.07-30 | IT-SPME-HPLC-DAD |
IL modified MF aerogel[ | five estrogens | water, aloe | 0.05-0.20 | 0.15-20 | IT-SPME-HPLC-DAD |
RF aerogel[ | five estrogens | water | 0.005-0.030 | 0.017-20 | IT-SPME-HPLC-DAD |
Al(Ⅲ)-MOA[ | BTEX, five phenols | water | - | - | HS-SPME-GC-MS |
MOA[ | five chlorobenzenes | river and tap water, | 0.0001-0.06 | 0.0004-20 | HS-SPME-GC-ECD |
sludge and coastal soil |
Adsorbents | Analytes | Samples | LOD/(μg/L) | Linear range/ (μg/L) | Analytical method |
---|---|---|---|---|---|
Tetraazacalix[2]arene[2]triazine | five PAHs | river water | 0.0004 | 0.0005-0.1 | SPE-HPLC-FLD |
bonded silica[ | Cu(Ⅱ) | 0.015 | 0.1-100 | SPE-graphite furnace atomic absorption spectrometry | |
Tetraazacalix[2]arene[2]triazine coated Fe3O4/Si | five PAHs | surface water and ground water | 0.00009-0.00015 | 0.0005-0.05 | MSPE-HPLC-FLD |
six nitroaromatics | 0.006-0.011 | 0.02-0.2 | MSPE-HPLC-UV | ||
four metal ions | 0.017-0.053 | 0.02-2.0 | MSPE-atomic absorption spectrometry | ||
Melamine sponge functionalized with urea-formaldehyde co-oligomers[ | ten hydrophobic analytes | lake water | 0.01 | 1.0-100 | SPE-HPLC-DAD |
Melamine sponge decorated with copper sheets[ | ten sulfonamides | lake water | 0.008 | 0.5-150 | SPE-HPLC-DAD |
Triazine-based polymeric modified Fe3O4/GO[ | acidic and basic pesticides | water samples | 0.17 | 5.0-500 | MSPE-HPLC-UV |
Magnetic covalent triazine-based frameworks[ | six perfluorinated acids | water samples | 0.00062 | 0.005-4.0 | MSPE-HPLC-MS/MS |
Triazine-cored covalent organic framework[ | five polybrominated diphenyl ethers | water samples | 0.00003 | 0.0001-5.0 | DSPE-GC-MS/MS |
Covalent triazine-based framework- grafted functionalized fibrous silica sphere[ | chlorpyrifos fenthion | water samples | 0.05 0.55 | 0.1-1 1.0-700 | SPME-ion mobility spectrometry |
Triazine-based covalent organic framework[ | nine antibiotics | water samples | 0.031 | 1-500 | SPE-UPLC-MS/MS |
Triazine-based organic polymers@ SiO2 nanospheres[ | eight PAHs | water samples | 0.003 | 0.01-20 | IT-SPME-HPLC-DAD |
Triazine-based covalent porous organic polymer[ | eight PAHs | water samples | 0.004 | 0.013-20 | IT-SPME-HPLC-DAD |
Table 5 Recent applications of triazinyl-based adsorbents for sample preparation in analysis and detection of environmental pollutants
Adsorbents | Analytes | Samples | LOD/(μg/L) | Linear range/ (μg/L) | Analytical method |
---|---|---|---|---|---|
Tetraazacalix[2]arene[2]triazine | five PAHs | river water | 0.0004 | 0.0005-0.1 | SPE-HPLC-FLD |
bonded silica[ | Cu(Ⅱ) | 0.015 | 0.1-100 | SPE-graphite furnace atomic absorption spectrometry | |
Tetraazacalix[2]arene[2]triazine coated Fe3O4/Si | five PAHs | surface water and ground water | 0.00009-0.00015 | 0.0005-0.05 | MSPE-HPLC-FLD |
six nitroaromatics | 0.006-0.011 | 0.02-0.2 | MSPE-HPLC-UV | ||
four metal ions | 0.017-0.053 | 0.02-2.0 | MSPE-atomic absorption spectrometry | ||
Melamine sponge functionalized with urea-formaldehyde co-oligomers[ | ten hydrophobic analytes | lake water | 0.01 | 1.0-100 | SPE-HPLC-DAD |
Melamine sponge decorated with copper sheets[ | ten sulfonamides | lake water | 0.008 | 0.5-150 | SPE-HPLC-DAD |
Triazine-based polymeric modified Fe3O4/GO[ | acidic and basic pesticides | water samples | 0.17 | 5.0-500 | MSPE-HPLC-UV |
Magnetic covalent triazine-based frameworks[ | six perfluorinated acids | water samples | 0.00062 | 0.005-4.0 | MSPE-HPLC-MS/MS |
Triazine-cored covalent organic framework[ | five polybrominated diphenyl ethers | water samples | 0.00003 | 0.0001-5.0 | DSPE-GC-MS/MS |
Covalent triazine-based framework- grafted functionalized fibrous silica sphere[ | chlorpyrifos fenthion | water samples | 0.05 0.55 | 0.1-1 1.0-700 | SPME-ion mobility spectrometry |
Triazine-based covalent organic framework[ | nine antibiotics | water samples | 0.031 | 1-500 | SPE-UPLC-MS/MS |
Triazine-based organic polymers@ SiO2 nanospheres[ | eight PAHs | water samples | 0.003 | 0.01-20 | IT-SPME-HPLC-DAD |
Triazine-based covalent porous organic polymer[ | eight PAHs | water samples | 0.004 | 0.013-20 | IT-SPME-HPLC-DAD |
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