色谱 ›› 2021, Vol. 39 ›› Issue (8): 781-801.DOI: 10.3724/SP.J.1123.2021.02030
冯娟娟, 纪香平, 李春英, 孙明霞, 韩森, 冯加庆, 孙海丽, 冯洋, 孙敏*()
收稿日期:
2021-02-28
出版日期:
2021-08-08
发布日期:
2021-06-29
通讯作者:
孙敏
作者简介:
*Tel:(0531)82765475,E-mail: chm_sunm@ujn.edu.cn.基金资助:
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:
摘要:
针对复杂样品的分析和痕量目标物的检测,样品前处理是必不可少的,高效的样品前处理技术不仅可以去除或减小样品基质干扰而且能够实现分析物的富集,提高分析检测的准确性和灵敏度。近年来,固相萃取、磁分散固相萃取、枪头固相萃取、搅拌棒萃取、固相微萃取等高效的样品前处理技术已在环境污染物分析检测中获得广泛关注,萃取效率主要取决于萃取材料,所以新型的高效萃取材料一直是样品前处理研究领域的重要发展方向。该文总结和讨论了近年来新型样品前处理材料在环境污染物分析检测中的研究进展,主要聚焦在石墨烯、氧化石墨烯、碳纳米管、无机气凝胶、有机气凝胶、三嗪基功能材料、三嗪基聚合物、分子印迹聚合物、共价有机框架材料、金属有机框架材料以及它们的功能化萃取材料等。这些材料已经被应用于环境样品中不同类别污染物的萃取富集,如重金属离子、多环芳烃、塑化剂、烷烃、苯酚、氯酚、氯苯、多溴联苯醚、全氟磺酸、全氟羧酸、雌激素、药物残留、农药残留等。这些样品前处理材料具有高的表面积、大量的吸附位点,并涉及多种萃取机理如π-π、静电、疏水、亲水、氢键、卤键等相互作用。基于这些萃取材料的多种样品前处理技术与各类检测方法如色谱、质谱、原子吸收光谱、荧光光谱、离子迁移谱等相结合,已广泛应用于环境污染物的高灵敏分析检测。最后,该文总结了样品前处理发展中存在的问题,并展望了其未来在环境分析中的发展趋势。
中图分类号:
冯娟娟, 纪香平, 李春英, 孙明霞, 韩森, 冯加庆, 孙海丽, 冯洋, 孙敏. 新型样品前处理材料在环境污染物分析检测中的研究进展[J]. 色谱, 2021, 39(8): 781-801.
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.
图1 新型样品前处理材料在环境污染物分析检测中的研究进展
Fig. 1 Recent advance of some new sample pretreatment materials in the 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 |
表1 石墨烯和氧化石墨烯基样品前处理材料在环境污染物分析检测中的应用
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 |
表2 碳纳米管基样品前处理材料在环境污染物分析检测中的应用
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 |
表 3 无机气凝胶样品前处理材料在环境污染物分析检测中的应用
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 |
表4 有机气凝胶样品前处理材料在环境污染物分析检测中的应用
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 |
表 5 三嗪基吸附剂作为样品前处理材料在环境污染物分析检测中的应用
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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