Chinese Journal of Chromatography ›› 2021, Vol. 39 ›› Issue (1): 34-45.DOI: 10.3724/SP.J.1123.2020.07025
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WANG Xingyi1,2, CHEN Yanlong1, XIAO Xiaohua1,*(
), LI Gongke1,*(
)
Received:2020-08-13
Online:2021-01-08
Published:2020-12-20
Contact:
XIAO Xiaohua,LI Gongke
Supported by:CLC Number:
WANG Xingyi, CHEN Yanlong, XIAO Xiaohua, LI Gongke. Recent advances in sample preparation technologies for analysis of harmful substances in aquatic products[J]. Chinese Journal of Chromatography, 2021, 39(1): 34-45.
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URL: https://www.chrom-china.com/EN/10.3724/SP.J.1123.2020.07025
Fig. 1 Distribution of literatures of sample preparation technologies for harmful substances analysis in aquatic products published during 2010-2020 LLE: liquid-liquid extraction; SPE: solid-phase extraction; SPME: solid-phase microextraction; QuEChERS: quick, easy, cheap, effective, rugged, and safe method; MSPE: magnetic solid-phase extraction. Data source: Web of science and CNKI; keywords: sample pretreatment or sample extraction; liquid-liquid extraction or LLE; solid-phase extraction or SPE; solid-phase microextraction or SPME; magnetic solid-phase extraction or MSPE; QuEChERS; aquatic product; seafood; shellfish.
Fig. 2 Schematic of preparation of SPME coating[30] TFPB: 1,3,5-tris(4-formylphenyl)benzene; BD: benzidine; RT: room temperature; APTES: 3-aminopropyltriethoxysilane; SS: a stainless steel wire fiber.
| Preparation technology | Sample | Analyte | Analytical method | LOD | Ref. | |
|---|---|---|---|---|---|---|
| LLE | shrimp | PCBs | GC-MS | 0.02-0.14 | μg/L | [ |
| ASE | fish | PCBs | GC-MS | 0.1-0.5 | ng/kg | [ |
| SPME | fish, shrimp | PCBs | GC-MS | 0.07-0.35 | ng/L | [ |
| MSPE | fish | PCBs | GC-MS | 0.061-0.096 | ng/g | [ |
| ULLE | fish | PAHs | GC-MS | 0.12-0.25 | μg/kg | [ |
| QuEChERS | shrimp, crab | PAHs | HPLC-FLD | 0.2-2.0 | μg/kg | [ |
| SPE | shellfish | PAHs | HPLC-VWD/FLD | 0.5 | μg/kg | [ |
| SPME | fish | PAHs | GC-MS | 0.11-1.40 | μg/kg | [ |
| LLE | fish, shrimp | chlorinated phenols | GC-MS | 0.78 | μg/kg | [ |
| SPE | shrimp, crab | pentachlorophenol | HPLC-MS | 0.2 | μg/kg | [ |
| MSPE | shrimp | phenolic endocrine | HPLC-FLD | 1.4-8.7 | μg/L | [ |
| QuEChERS | fish, shellfish | PFASs | LC-MS/MS | 0.006-0.02 | μg/kg | [ |
| SPE | fish | PFASs | UPLC-MS/MS | 2-120 | pg/g | [ |
| LLE | shellfish | Pesticide | GC-MS/MS | 0.7-3.3 | μg/kg | [ |
| MIP-SPE | fish | pyrethroid insecticide | GC-ECD | 16.1-26.5 | ng/kg | [ |
| SPME | fish | sulfonamides | UPLC-MS/MS | 1.3-4.7 | ng/L | [ |
| MSPE | shrimp | sulfonamides | UPLC-VWD | 0.2-1 | ng/mL | [ |
| LLE | fish | Hg | HPLC-ICP-MS | 0.09-0.18 | ng/mL | [ |
| DLLME-SFO | fish | Cd, Pb | GFAAS | 0.04-0.1 | μg/kg | [ |
| SPE | fish | Pb, Cu | ICP-OES | 1.434, 0.048 | μg/L | [ |
| IIPs-SPE | fish | Cd, Pb | ETAAS | 0.15, 0.5 | μg/L | [ |
| MSPE | fish | Ag, Cd, Pb, Hg, Cu | ICP-OES | 0.01-0.09 | ng/mL | [ |
| MR/IT-SPME | fish | Cu, Co, Hg | HPLC-DAD | 0.69-4.9 | μg/kg | [ |
Table 1 Sample preparation technologies for analysis of environmental pollutants in aquatic products
| Preparation technology | Sample | Analyte | Analytical method | LOD | Ref. | |
|---|---|---|---|---|---|---|
| LLE | shrimp | PCBs | GC-MS | 0.02-0.14 | μg/L | [ |
| ASE | fish | PCBs | GC-MS | 0.1-0.5 | ng/kg | [ |
| SPME | fish, shrimp | PCBs | GC-MS | 0.07-0.35 | ng/L | [ |
| MSPE | fish | PCBs | GC-MS | 0.061-0.096 | ng/g | [ |
| ULLE | fish | PAHs | GC-MS | 0.12-0.25 | μg/kg | [ |
| QuEChERS | shrimp, crab | PAHs | HPLC-FLD | 0.2-2.0 | μg/kg | [ |
| SPE | shellfish | PAHs | HPLC-VWD/FLD | 0.5 | μg/kg | [ |
| SPME | fish | PAHs | GC-MS | 0.11-1.40 | μg/kg | [ |
| LLE | fish, shrimp | chlorinated phenols | GC-MS | 0.78 | μg/kg | [ |
| SPE | shrimp, crab | pentachlorophenol | HPLC-MS | 0.2 | μg/kg | [ |
| MSPE | shrimp | phenolic endocrine | HPLC-FLD | 1.4-8.7 | μg/L | [ |
| QuEChERS | fish, shellfish | PFASs | LC-MS/MS | 0.006-0.02 | μg/kg | [ |
| SPE | fish | PFASs | UPLC-MS/MS | 2-120 | pg/g | [ |
| LLE | shellfish | Pesticide | GC-MS/MS | 0.7-3.3 | μg/kg | [ |
| MIP-SPE | fish | pyrethroid insecticide | GC-ECD | 16.1-26.5 | ng/kg | [ |
| SPME | fish | sulfonamides | UPLC-MS/MS | 1.3-4.7 | ng/L | [ |
| MSPE | shrimp | sulfonamides | UPLC-VWD | 0.2-1 | ng/mL | [ |
| LLE | fish | Hg | HPLC-ICP-MS | 0.09-0.18 | ng/mL | [ |
| DLLME-SFO | fish | Cd, Pb | GFAAS | 0.04-0.1 | μg/kg | [ |
| SPE | fish | Pb, Cu | ICP-OES | 1.434, 0.048 | μg/L | [ |
| IIPs-SPE | fish | Cd, Pb | ETAAS | 0.15, 0.5 | μg/L | [ |
| MSPE | fish | Ag, Cd, Pb, Hg, Cu | ICP-OES | 0.01-0.09 | ng/mL | [ |
| MR/IT-SPME | fish | Cu, Co, Hg | HPLC-DAD | 0.69-4.9 | μg/kg | [ |
| Preparation technology | Sample | Analyte | Analytical method | LOD | Ref. | |
|---|---|---|---|---|---|---|
| MAE-LLE | fish | steroid hormones | LC-MS | 0.03-0.15 | ng/g | [ |
| QuEChERS | fish, shrimp | hormones | UPLC-MS | 0.2-2.7 | μg/kg | [ |
| MAE-SPE | fish | steroid hormones | UPLC-MS/MS | 0.14-49.0 | ng/g | [ |
| MIP-SPE | fish, shrimp | estrogens | HPLC-FLD | 0.023 | mg/L | [ |
| LLE | shrimp | nitrofuran | HPLC-FLD | 0.24-0.26 | μg/kg | [ |
| IL-DLLME | fish | fluoroquinolones | HPLC-DAD | 0.5-1.1 | ng/mL | [ |
| QuEChERS | fish, shrimp | chlorpyrifos | HPLC-MS/MS | 0.25 | μg/kg | [ |
| SPE | fish | florfenicol amine | LC-MS/MS | 0.13-1.64 | μg/kg | [ |
| MIP-MSPE | fish, shrimp | macrolide | HPLC-UV | 0.015-0.2 | μg/g | [ |
| MSPE | fish | nitrofurantoin | SERS | 0.014 | mg/L | [ |
| SPME | fish | fluoroquinolones | LC-MS | 0.3-1.5 | ng/g | [ |
| DLLME | fish | menthol | GC-MS | 0.0539 | μg/L | [ |
| QuEChERS | fish | tricaine mesylate | HPLC-MS/MS | 2.5 | μg/kg | [ |
| SPE | fish, shrimp | diazepam | UPLC-MS | 0.5 | μg/kg | [ |
| SPE | fish, shrimp | eugenol | UPLC-MS | 0.3-0.75 | μg/kg | [ |
| SPME | fish | anesthetics | GC-MS | 1.7-9.4 | ng/g | [ |
| SPME | fish | 2-phenoxyethanol | HPLC-MS | 0.18 | μg/mL | [ |
| LLE | fish | 4-hexylresorcinol | UPLC-FLD | 2.0 | mg/kg | [ |
| LLE | squid | formaldehyde | GC-MS | 2.0 | mg/kg | [ |
| SPME | fish | formaldehyde | GC-MS | 17 | μg/kg | [ |
| HS-SPME | fish | trihalomethanes | GC-MS | 0.11-0.35 | μg/kg | [ |
Table 2 Sample pretreatment technologies for analysis of harmful substances added during aquaculture and transportation in aquatic products
| Preparation technology | Sample | Analyte | Analytical method | LOD | Ref. | |
|---|---|---|---|---|---|---|
| MAE-LLE | fish | steroid hormones | LC-MS | 0.03-0.15 | ng/g | [ |
| QuEChERS | fish, shrimp | hormones | UPLC-MS | 0.2-2.7 | μg/kg | [ |
| MAE-SPE | fish | steroid hormones | UPLC-MS/MS | 0.14-49.0 | ng/g | [ |
| MIP-SPE | fish, shrimp | estrogens | HPLC-FLD | 0.023 | mg/L | [ |
| LLE | shrimp | nitrofuran | HPLC-FLD | 0.24-0.26 | μg/kg | [ |
| IL-DLLME | fish | fluoroquinolones | HPLC-DAD | 0.5-1.1 | ng/mL | [ |
| QuEChERS | fish, shrimp | chlorpyrifos | HPLC-MS/MS | 0.25 | μg/kg | [ |
| SPE | fish | florfenicol amine | LC-MS/MS | 0.13-1.64 | μg/kg | [ |
| MIP-MSPE | fish, shrimp | macrolide | HPLC-UV | 0.015-0.2 | μg/g | [ |
| MSPE | fish | nitrofurantoin | SERS | 0.014 | mg/L | [ |
| SPME | fish | fluoroquinolones | LC-MS | 0.3-1.5 | ng/g | [ |
| DLLME | fish | menthol | GC-MS | 0.0539 | μg/L | [ |
| QuEChERS | fish | tricaine mesylate | HPLC-MS/MS | 2.5 | μg/kg | [ |
| SPE | fish, shrimp | diazepam | UPLC-MS | 0.5 | μg/kg | [ |
| SPE | fish, shrimp | eugenol | UPLC-MS | 0.3-0.75 | μg/kg | [ |
| SPME | fish | anesthetics | GC-MS | 1.7-9.4 | ng/g | [ |
| SPME | fish | 2-phenoxyethanol | HPLC-MS | 0.18 | μg/mL | [ |
| LLE | fish | 4-hexylresorcinol | UPLC-FLD | 2.0 | mg/kg | [ |
| LLE | squid | formaldehyde | GC-MS | 2.0 | mg/kg | [ |
| SPME | fish | formaldehyde | GC-MS | 17 | μg/kg | [ |
| HS-SPME | fish | trihalomethanes | GC-MS | 0.11-0.35 | μg/kg | [ |
| Preparation technology | Sample | Analyte | Analytical method | LOD | Ref. | |
|---|---|---|---|---|---|---|
| SPE | shellfish | yessotoxin | LC-MS/MS | 0.15-0.30 | μg/kg | [ |
| SPE | shellfish | shellfish toxin | LC-MS/MS | 0.1-1.1 | μg/kg | [ |
| QuEChERS | shellfish | shellfish toxin | UPLC-MS/MS | 0.3 | μg/kg | [ |
| QuEChERS | shellfish | marine toxin | UPLC-MS/MS | 0.10-1.47 | μg/kg | [ |
| MSPE | shellfish | domoic acid | HPLC-MS/MS | 1.45 | pg/mL | [ |
| MSPE | shellfish | domoic acid | HPLC-MS/MS | 0.2 | pg/mL | [ |
| SPME | fish | biogenic amines | GC-MS | 2.98-45.3 | μg/kg | [ |
| SPE | pufferfish | tetrodotoxin | LC-MS/MS | 2.3 | ng/g | [ |
Table 3 Sample preparation technologies for analysis of biotoxins in aquatic products
| Preparation technology | Sample | Analyte | Analytical method | LOD | Ref. | |
|---|---|---|---|---|---|---|
| SPE | shellfish | yessotoxin | LC-MS/MS | 0.15-0.30 | μg/kg | [ |
| SPE | shellfish | shellfish toxin | LC-MS/MS | 0.1-1.1 | μg/kg | [ |
| QuEChERS | shellfish | shellfish toxin | UPLC-MS/MS | 0.3 | μg/kg | [ |
| QuEChERS | shellfish | marine toxin | UPLC-MS/MS | 0.10-1.47 | μg/kg | [ |
| MSPE | shellfish | domoic acid | HPLC-MS/MS | 1.45 | pg/mL | [ |
| MSPE | shellfish | domoic acid | HPLC-MS/MS | 0.2 | pg/mL | [ |
| SPME | fish | biogenic amines | GC-MS | 2.98-45.3 | μg/kg | [ |
| SPE | pufferfish | tetrodotoxin | LC-MS/MS | 2.3 | ng/g | [ |
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