Chinese Journal of Chromatography ›› 2024, Vol. 42 ›› Issue (10): 979-989.DOI: 10.3724/SP.J.1123.2023.11002
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LI Yuankun1, HUANG Chaonan1, ZHOU Qian2, CHENG Jiawen1, MA Jiping1,*()
Received:
2023-11-03
Online:
2024-10-08
Published:
2024-09-27
Supported by:
CLC Number:
LI Yuankun, HUANG Chaonan, ZHOU Qian, CHENG Jiawen, MA Jiping. Determination of three dechloranes in environmental water by magnetic solid-phase extraction-gas chromatography-negative chemical ionization mass spectrometry based on the covalent organic framework material[J]. Chinese Journal of Chromatography, 2024, 42(10): 979-989.
Analyte | Retention time/min | Mr | Quantitative ion (m/z) | Qualitative ions (m/z) |
---|---|---|---|---|
Dechlorane 603 (Dec 603) | 26.57 | 637.6 | 637.6 | 635.6, 639.6 |
syn-Dechlorane plus (syn-DP) | 30.73 | 653.7 | 635.6 | 651.6, 655.6 |
anti-Dechlorane plus (anti-DP) | 32.14 | 653.7 | 635.6 | 651.6, 655.6 |
Table 1 Retention times and MS parameters of the three dechloranes
Analyte | Retention time/min | Mr | Quantitative ion (m/z) | Qualitative ions (m/z) |
---|---|---|---|---|
Dechlorane 603 (Dec 603) | 26.57 | 637.6 | 637.6 | 635.6, 639.6 |
syn-Dechlorane plus (syn-DP) | 30.73 | 653.7 | 635.6 | 651.6, 655.6 |
anti-Dechlorane plus (anti-DP) | 32.14 | 653.7 | 635.6 | 651.6, 655.6 |
Fig. 6 (a) Adsorption kinetic curve, (b) pseudo-first-order kinetic and (c) pseudo-second-order kinetic adsorption kinetics fitting curves of Fe3O4@TpBD for syn-DP
Fig. 8 Effects of (a) dosage of Fe3O4@TpBD, (b) pH of water sample, (c) extraction time, (d) elution solvent type, (e) elution solvent volume, (f) elution time and (g) mass fraction of NaCl on the recoveries of the three target analytes (n=3)
Analyte | Linear range/(ng/L) | Linear equation | r2 | LOD/(ng/L) | LOQ/(ng/L) |
---|---|---|---|---|---|
Dec 603 | 2-1000 | y=19.94x-86.59 | 0.9974 | 0.18 | 0.60 |
syn-DP | 2-1000 | y=1.96x+60.18 | 0.9997 | 0.22 | 0.73 |
anti-DP | 2-1000 | y=7.71x-54.27 | 0.9978 | 0.27 | 0.92 |
Table 2 Linear ranges, correlation coefficients (r2), limits of detection (LODs) and quantification (LOQs) of the three target analytes
Analyte | Linear range/(ng/L) | Linear equation | r2 | LOD/(ng/L) | LOQ/(ng/L) |
---|---|---|---|---|---|
Dec 603 | 2-1000 | y=19.94x-86.59 | 0.9974 | 0.18 | 0.60 |
syn-DP | 2-1000 | y=1.96x+60.18 | 0.9997 | 0.22 | 0.73 |
anti-DP | 2-1000 | y=7.71x-54.27 | 0.9978 | 0.27 | 0.92 |
Analyte | Spiked level/ (ng/L) | Recovery/ % | Intra-day RSD/% | Inter-day RSD/% |
---|---|---|---|---|
Dec 603 | 8 | 108.0 | 4.2 | 9.4 |
50 | 106.3 | 16.2 | 15.7 | |
200 | 97.6 | 14.9 | 14.5 | |
syn-DP | 8 | 96.4 | 5.5 | 9.0 |
50 | 86.6 | 15.2 | 6.9 | |
200 | 81.0 | 9.6 | 9.2 | |
anti-DP | 8 | 98.5 | 10.8 | 8.7 |
50 | 97.9 | 15.1 | 12.0 | |
200 | 79.8 | 11.5 | 7.2 |
Table 3 Recoveries, intra- and inter-day RSDs of the three dechloranes (n=6)
Analyte | Spiked level/ (ng/L) | Recovery/ % | Intra-day RSD/% | Inter-day RSD/% |
---|---|---|---|---|
Dec 603 | 8 | 108.0 | 4.2 | 9.4 |
50 | 106.3 | 16.2 | 15.7 | |
200 | 97.6 | 14.9 | 14.5 | |
syn-DP | 8 | 96.4 | 5.5 | 9.0 |
50 | 86.6 | 15.2 | 6.9 | |
200 | 81.0 | 9.6 | 9.2 | |
anti-DP | 8 | 98.5 | 10.8 | 8.7 |
50 | 97.9 | 15.1 | 12.0 | |
200 | 79.8 | 11.5 | 7.2 |
Fig. 11 Chromatograms of laboratory tap water samples (spiked level 40 ng/L) (a) before and (b) after enrichment by magnetic solid-phase extraction (MSPE)
Analysis method | Pretreatment method | Matrices | Analytes | Pretreatment time | Organic reagent dosage/mL | LODs/ (ng/L) | Ref. | |||
---|---|---|---|---|---|---|---|---|---|---|
GC-NCI/MS | LLE | seawater | Dec 602, Dec 603, Dec 604, syn-DP, anti-DP | >10 min | 200 | 0.01- | 0.1 | [ | ||
GC-NCI/MS | LLE | aquaculture water | syn-DP, anti-DP | 1 h | 300 | 52- | 66 | [ | ||
GC-ECNI/MS | SPE | drinking water | Dec 602, Dec 603, syn-DP, anti-DP | >1 h | >30 | 0.19- | 0.44 | [ | ||
GC-EI/MS | vortex | adhesives | syn-DP, anti-DP | 10 min | 30 | 43- | 56 | [ | ||
GC-NCI/MS | MSPE | laboratory tap water, reservoir water, wastewater treatment plant effluent, landfill leachate treatment effluent | Dec 603, syn-DP, anti-DP | 16 min | 2 | 0.18- | 0.27 | this work |
Table 4 Comparison of this method with literature methods
Analysis method | Pretreatment method | Matrices | Analytes | Pretreatment time | Organic reagent dosage/mL | LODs/ (ng/L) | Ref. | |||
---|---|---|---|---|---|---|---|---|---|---|
GC-NCI/MS | LLE | seawater | Dec 602, Dec 603, Dec 604, syn-DP, anti-DP | >10 min | 200 | 0.01- | 0.1 | [ | ||
GC-NCI/MS | LLE | aquaculture water | syn-DP, anti-DP | 1 h | 300 | 52- | 66 | [ | ||
GC-ECNI/MS | SPE | drinking water | Dec 602, Dec 603, syn-DP, anti-DP | >1 h | >30 | 0.19- | 0.44 | [ | ||
GC-EI/MS | vortex | adhesives | syn-DP, anti-DP | 10 min | 30 | 43- | 56 | [ | ||
GC-NCI/MS | MSPE | laboratory tap water, reservoir water, wastewater treatment plant effluent, landfill leachate treatment effluent | Dec 603, syn-DP, anti-DP | 16 min | 2 | 0.18- | 0.27 | this work |
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