Chinese Journal of Chromatography ›› 2023, Vol. 41 ›› Issue (5): 409-416.DOI: 10.3724/SP.J.1123.2022.09016
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SONG Xinli*(), WANG Ning, HE Feiyan, CHENG Canling, WANG Fei, WANG Jinglong, ZHANG Lihua
Received:
2022-09-16
Online:
2023-05-08
Published:
2023-04-23
Supported by:
CLC Number:
SONG Xinli, WANG Ning, HE Feiyan, CHENG Canling, WANG Fei, WANG Jinglong, ZHANG Lihua. Determination of trace perfluorinated compounds in environmental water samples by dispersive solid- phase extraction-high performance liquid chromatography-tandem mass spectrometry using carbon nanotube composite materials[J]. Chinese Journal of Chromatography, 2023, 41(5): 409-416.
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URL: https://www.chrom-china.com/EN/10.3724/SP.J.1123.2022.09016
Compound | Retention time/min | Quantitive ion pair | Qualitative ion pair | ||||
---|---|---|---|---|---|---|---|
Collision energy/eV | Monitored transition (m/z) | Collision energy/eV | Monitored transition (m/z) | ||||
Perfluoroheptanoic acid (PFHpA) | 5.7 | -14 | 362.9/319.1 | -24 | 362.9/169.0 | ||
Perfluorohexane sulfonate (PFHxS) | 5.8 | -14 | 399.0/79.8 | -24 | 399.0/99.0 | ||
Perfluorooctanoic acid (PFOA) | 6.7 | -16 | 413.1/368.9 | -24 | 413.1/169.1 | ||
Perfluorononanoic acid (PFNA) | 7.6 | -18 | 462.9/418.9 | -26 | 462.9/219.1 | ||
Perfluorooctane sulfonate (PFOS) | 7.6 | -52 | 499.0/79.9 | -57 | 499.0/99.0 | ||
Perfluorodecanoic acid (PFDA) | 8.3 | -62 | 512.9/468.9 | -67 | 512.9/218.7 |
Table 1 MS parameters of the six perfluorinated compounds (PFCs)
Compound | Retention time/min | Quantitive ion pair | Qualitative ion pair | ||||
---|---|---|---|---|---|---|---|
Collision energy/eV | Monitored transition (m/z) | Collision energy/eV | Monitored transition (m/z) | ||||
Perfluoroheptanoic acid (PFHpA) | 5.7 | -14 | 362.9/319.1 | -24 | 362.9/169.0 | ||
Perfluorohexane sulfonate (PFHxS) | 5.8 | -14 | 399.0/79.8 | -24 | 399.0/99.0 | ||
Perfluorooctanoic acid (PFOA) | 6.7 | -16 | 413.1/368.9 | -24 | 413.1/169.1 | ||
Perfluorononanoic acid (PFNA) | 7.6 | -18 | 462.9/418.9 | -26 | 462.9/219.1 | ||
Perfluorooctane sulfonate (PFOS) | 7.6 | -52 | 499.0/79.9 | -57 | 499.0/99.0 | ||
Perfluorodecanoic acid (PFDA) | 8.3 | -62 | 512.9/468.9 | -67 | 512.9/218.7 |
Fig. 3 Effects of (a) adsorption time, (b) amount of adsorbent, (c) sample pH value and (d) ionic strength on the extraction efficiencies of the six PFCs (n=5)
Fig. 4 Effects of (a) desorption solvent, (b) volume of desorption solvent and (c) desorption time on the extraction efficiencies of the six PFCs (n=5)
Compound | Linear range/ (ng/L) | r | LOD/ (ng/L) | LOQ/ (ng/L) |
---|---|---|---|---|
PFHpA | 0.9-1000 | 0.973 | 0.26 | 0.87 |
PFHxS | 0.7-1000 | 0.986 | 0.20 | 0.67 |
PFOA | 0.6-1000 | 0.982 | 0.18 | 0.60 |
PFNA | 0.4-1000 | 0.992 | 0.11 | 0.37 |
PFOS | 0.4-1000 | 0.996 | 0.10 | 0.33 |
PFDA | 0.4-1000 | 0.997 | 0.10 | 0.33 |
Table 2 Linear ranges, correlation coefficients (r), LODs and LOQs of the six PFCs
Compound | Linear range/ (ng/L) | r | LOD/ (ng/L) | LOQ/ (ng/L) |
---|---|---|---|---|
PFHpA | 0.9-1000 | 0.973 | 0.26 | 0.87 |
PFHxS | 0.7-1000 | 0.986 | 0.20 | 0.67 |
PFOA | 0.6-1000 | 0.982 | 0.18 | 0.60 |
PFNA | 0.4-1000 | 0.992 | 0.11 | 0.37 |
PFOS | 0.4-1000 | 0.996 | 0.10 | 0.33 |
PFDA | 0.4-1000 | 0.997 | 0.10 | 0.33 |
Compound | 20 ng/L | 100 ng/L | 500 ng/L | |||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
Intra-day RSD/% | Inter-day RSD/% | Intra-day RSD/% | Inter-day RSD/% | Intra-day RSD/% | Inter-day RSD/% | |||||||||
PFHpA | 7.75 | 8.21 | 6.14 | 8.82 | 5.47 | 7.32 | ||||||||
PFHxS | 6.23 | 7.80 | 8.46 | 9.14 | 7.48 | 9.63 | ||||||||
PFOA | 5.92 | 8.15 | 7.85 | 9.02 | 7.03 | 8.61 | ||||||||
PFNA | 4.71 | 5.37 | 5.29 | 6.71 | 3.64 | 4.29 | ||||||||
PFOS | 2.73 | 3.38 | 3.82 | 5.52 | 4.43 | 4.82 | ||||||||
PFDA | 3.34 | 3.91 | 2.95 | 4.16 | 2.51 | 3.59 |
Table 3 Intra-day and inter-day precisions of the six PFCs (n=3)
Compound | 20 ng/L | 100 ng/L | 500 ng/L | |||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
Intra-day RSD/% | Inter-day RSD/% | Intra-day RSD/% | Inter-day RSD/% | Intra-day RSD/% | Inter-day RSD/% | |||||||||
PFHpA | 7.75 | 8.21 | 6.14 | 8.82 | 5.47 | 7.32 | ||||||||
PFHxS | 6.23 | 7.80 | 8.46 | 9.14 | 7.48 | 9.63 | ||||||||
PFOA | 5.92 | 8.15 | 7.85 | 9.02 | 7.03 | 8.61 | ||||||||
PFNA | 4.71 | 5.37 | 5.29 | 6.71 | 3.64 | 4.29 | ||||||||
PFOS | 2.73 | 3.38 | 3.82 | 5.52 | 4.43 | 4.82 | ||||||||
PFDA | 3.34 | 3.91 | 2.95 | 4.16 | 2.51 | 3.59 |
Adsorption materials | Extraction method | Analytical method | Linear range/ (ng/L) | LOD/ (ng/L) | Analytes | |
---|---|---|---|---|---|---|
MOFs[ | d-SPE | LC-MS/MS | 1-2000 | 0.30-2.00 | PFHpA, PFHxS, PFOA, PFNA, PFOS, PFDA, PFBA, | |
Bamboo charcoal[ | SPE | LC-MS/MS | 1-1000 | 0.20 | PFOA | |
COFs[ | MSPE | LC-MS/MS | 5-4000 | 0.62-1.39 | PFHpA, PFPeA, PFOA, PFNA, PFDA, PFBA, | |
EG-silicone[ | SBSE | LC-MS/MS | 7-177 | 6-50 | PFHpA, PFHxA, PFOA, PFOS, PFBuA, PFPeA, | |
HLB[ | SPE | LC-MS/MS | 500-200000 | 150-900 | PFOS, PFOA, PFNA, PFDA | |
Oasis HLB[ | SPE | LC-ToF-MS | 0-250 | 1-100 | PFHpA, PFHxA, PFOA, PFNA, PFDA, PFOS, PFHxS, PFPeA | |
CNT@SiO2(this method) | d-SPE | LC-MS/MS | 0.4-1000 | 0.10-0.26 | PFHpA, PFHxS, PFOA, PFNA, PFOS, PFDA |
Table 4 Comparison of analysis methods of PFCs in water samples
Adsorption materials | Extraction method | Analytical method | Linear range/ (ng/L) | LOD/ (ng/L) | Analytes | |
---|---|---|---|---|---|---|
MOFs[ | d-SPE | LC-MS/MS | 1-2000 | 0.30-2.00 | PFHpA, PFHxS, PFOA, PFNA, PFOS, PFDA, PFBA, | |
Bamboo charcoal[ | SPE | LC-MS/MS | 1-1000 | 0.20 | PFOA | |
COFs[ | MSPE | LC-MS/MS | 5-4000 | 0.62-1.39 | PFHpA, PFPeA, PFOA, PFNA, PFDA, PFBA, | |
EG-silicone[ | SBSE | LC-MS/MS | 7-177 | 6-50 | PFHpA, PFHxA, PFOA, PFOS, PFBuA, PFPeA, | |
HLB[ | SPE | LC-MS/MS | 500-200000 | 150-900 | PFOS, PFOA, PFNA, PFDA | |
Oasis HLB[ | SPE | LC-ToF-MS | 0-250 | 1-100 | PFHpA, PFHxA, PFOA, PFNA, PFDA, PFOS, PFHxS, PFPeA | |
CNT@SiO2(this method) | d-SPE | LC-MS/MS | 0.4-1000 | 0.10-0.26 | PFHpA, PFHxS, PFOA, PFNA, PFOS, PFDA |
Compound | Added level/ (ng/L) | Recoveries/% | Compound | Added level/ (ng/L) | Recoveries/% | ||||
---|---|---|---|---|---|---|---|---|---|
Tap water | Barreled drinking water | River water | Tap water | Barreled drinking water | River water | ||||
PFHpA | 10 | 72.4±2.3 | 73.4±5.6 | 77.1±9.0 | PFNA | 10 | 85.4±3.3 | 82.8±7.5 | 85.1±2.9 |
100 | 72.1±2.5 | 74.1±5.0 | 72.9±8.0 | 100 | 84.1±3.1 | 85.5±3.1 | 83.8±3.7 | ||
500 | 74.2±4.1 | 77.0±8.0 | 80.3±7.9 | 500 | 82.1±1.9 | 85.2±6.9 | 91.9±7.3 | ||
PFHxS | 10 | 75.1±6.2 | 77.5±7.3 | 81.5±8.0 | PFOS | 10 | 87.2±5.9 | 93.1±6.1 | 103.0±8.5 |
100 | 76.6±8.5 | 81.1±4.4 | 79.3±3.8 | 100 | 93.5±5.1 | 100.8±9.6 | 90.6±8.0 | ||
500 | 80.6±2.9 | 79.6±6.9 | 76.7±2.9 | 500 | 86.8±4.5 | 92.9±8.1 | 89.6±8.0 | ||
PFOA | 10 | 83.6±6.1 | 76.1±6.2 | 81.0±4.1 | PFDA | 10 | 89.6±8.5 | 88.0±3.9 | 90.3±3.9 |
100 | 81.4±6.2 | 83.2±8.1 | 82.0±7.8 | 100 | 86.6±9.0 | 92.8±3.0 | 86.4±3.5 | ||
500 | 86.2±9.1 | 82.7±3.7 | 84.6±8.0 | 500 | 109.6±7.1 | 84.9±6.4 | 94.8±2.8 |
Table 5 Spiked recoveries of the six PFCs in environmental water samples (n=5)
Compound | Added level/ (ng/L) | Recoveries/% | Compound | Added level/ (ng/L) | Recoveries/% | ||||
---|---|---|---|---|---|---|---|---|---|
Tap water | Barreled drinking water | River water | Tap water | Barreled drinking water | River water | ||||
PFHpA | 10 | 72.4±2.3 | 73.4±5.6 | 77.1±9.0 | PFNA | 10 | 85.4±3.3 | 82.8±7.5 | 85.1±2.9 |
100 | 72.1±2.5 | 74.1±5.0 | 72.9±8.0 | 100 | 84.1±3.1 | 85.5±3.1 | 83.8±3.7 | ||
500 | 74.2±4.1 | 77.0±8.0 | 80.3±7.9 | 500 | 82.1±1.9 | 85.2±6.9 | 91.9±7.3 | ||
PFHxS | 10 | 75.1±6.2 | 77.5±7.3 | 81.5±8.0 | PFOS | 10 | 87.2±5.9 | 93.1±6.1 | 103.0±8.5 |
100 | 76.6±8.5 | 81.1±4.4 | 79.3±3.8 | 100 | 93.5±5.1 | 100.8±9.6 | 90.6±8.0 | ||
500 | 80.6±2.9 | 79.6±6.9 | 76.7±2.9 | 500 | 86.8±4.5 | 92.9±8.1 | 89.6±8.0 | ||
PFOA | 10 | 83.6±6.1 | 76.1±6.2 | 81.0±4.1 | PFDA | 10 | 89.6±8.5 | 88.0±3.9 | 90.3±3.9 |
100 | 81.4±6.2 | 83.2±8.1 | 82.0±7.8 | 100 | 86.6±9.0 | 92.8±3.0 | 86.4±3.5 | ||
500 | 86.2±9.1 | 82.7±3.7 | 84.6±8.0 | 500 | 109.6±7.1 | 84.9±6.4 | 94.8±2.8 |
Fig. 6 Chromatograms of (a) blank tap water and blank tap water spiked with (b) 10 ng/L and (c) 500 ng/L PFCs 1. PFHpA; 2. PFHxS; 3, PFOA; 4. PFNA; 5. PFOS; 6. PFDA.
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