Chinese Journal of Chromatography ›› 2021, Vol. 39 ›› Issue (8): 896-904.DOI: 10.3724/SP.J.1123.2021.01006
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JI Xuefeng1, LI Shuang1, WU Gege1, ZHAO Lin2, MA Jiping1,*()
Received:
2021-01-20
Online:
2021-08-08
Published:
2021-06-29
Contact:
MA Jiping
Supported by:
CLC Number:
JI Xuefeng, LI Shuang, WU Gege, ZHAO Lin, MA Jiping. Determination of seven phenoxy acid herbicides in water by dispersive solid phase extraction-ultra performance liquid chromatography-tandem mass spectrometry based on cationic metal-organic framework mixed matrix membrane[J]. Chinese Journal of Chromatography, 2021, 39(8): 896-904.
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URL: https://www.chrom-china.com/EN/10.3724/SP.J.1123.2021.01006
Analyte | tR/min | Precursor ions (m/z) | Product ions (m/z) | Declustering potentials/V | Collision energies/eV |
---|---|---|---|---|---|
4-Chlorophenoxyacetic acid (4-CPA) | 3.48 | 184.7*, 186.7 | 126.8, 128.9 | -50, -49 | -20, -20 |
4-Phenoxybutyric acid (PB) | 3.83 | 178.8* | 93.0 | -54 | -24 |
2,4-Dichlorophenoxyacetic acid (2,4-D) | 4.17 | 219.0*, 221.0 | 161.0, 163.0 | -40, -40 | -19, -19 |
2-Methyl-4-chlorophenoxyacetic acid (MCPA) | 4.29 | 199.0*, 201.0 | 141.0, 143.0 | -50, -50 | -22, -22 |
2,4,5-Trichlorophenoxyacetic acid (2,4,5-T) | 4.94 | 252.7*, 254.9 | 194.8, 196.7 | -45, -44 | -20, -22 |
2,4-Dichlorophenoxybutyric acid (2,4-DB) | 5.93 | 247.0*, 249.0 | 161.0, 163.0 | -40, -40 | -18, -21 |
2-(2,4,5-Trichlorophenoxy)propanoic acid (2,4,5-TP) | 6.09 | 266.8, 268.7* | 195.0, 196.9 | -48, -45 | -16, -25 |
Table 1 MS parameters of the seven phenoxy acid herbicides
Analyte | tR/min | Precursor ions (m/z) | Product ions (m/z) | Declustering potentials/V | Collision energies/eV |
---|---|---|---|---|---|
4-Chlorophenoxyacetic acid (4-CPA) | 3.48 | 184.7*, 186.7 | 126.8, 128.9 | -50, -49 | -20, -20 |
4-Phenoxybutyric acid (PB) | 3.83 | 178.8* | 93.0 | -54 | -24 |
2,4-Dichlorophenoxyacetic acid (2,4-D) | 4.17 | 219.0*, 221.0 | 161.0, 163.0 | -40, -40 | -19, -19 |
2-Methyl-4-chlorophenoxyacetic acid (MCPA) | 4.29 | 199.0*, 201.0 | 141.0, 143.0 | -50, -50 | -22, -22 |
2,4,5-Trichlorophenoxyacetic acid (2,4,5-T) | 4.94 | 252.7*, 254.9 | 194.8, 196.7 | -45, -44 | -20, -22 |
2,4-Dichlorophenoxybutyric acid (2,4-DB) | 5.93 | 247.0*, 249.0 | 161.0, 163.0 | -40, -40 | -18, -21 |
2-(2,4,5-Trichlorophenoxy)propanoic acid (2,4,5-TP) | 6.09 | 266.8, 268.7* | 195.0, 196.9 | -48, -45 | -16, -25 |
Fig. 4 Effects of (a) amounts of MOF, (b) values of sample pH, (c) extraction times, (d) ammonia concentrations in eluent, and (e) volumes of eluent on the extraction efficiencies of the seven phenoxy acid herbicides (n=3) MOF: metal-organic framework.
Analyte | Linear equation | r2 | Linear range/(μg/L) | LOD/(μg/L) | LOQ/(μg/L) |
---|---|---|---|---|---|
4-CPA | y=9.63×102x+2.29×103 | 0.9979 | 0.001-0.5 | 0.00013 | 0.00042 |
PB | y=1.85×102x+9.04×102 | 0.9981 | 0.005-0.5 | 0.00045 | 0.00150 |
2,4-D | y=7.74×102x+2.69×103 | 0.9998 | 0.001-0.5 | 0.00013 | 0.00042 |
MCPA | y=1.20×103x+1.44×103 | 0.9995 | 0.001-0.5 | 0.00010 | 0.00033 |
2,4,5-T | y=9.02×102x+2.87×103 | 0.9992 | 0.001-0.5 | 0.00015 | 0.00050 |
2,4-DB | y=2.77×102x+4.63×102 | 0.9999 | 0.005-0.5 | 0.00090 | 0.00300 |
2,4,5-TP | y=7.81×102x-5.87×102 | 0.9978 | 0.001-0.5 | 0.00015 | 0.00050 |
Table 2 Linear equations, correlation coefficients (r2), linear ranges, LODs and LOQs of the seven phenoxy acid herbicides
Analyte | Linear equation | r2 | Linear range/(μg/L) | LOD/(μg/L) | LOQ/(μg/L) |
---|---|---|---|---|---|
4-CPA | y=9.63×102x+2.29×103 | 0.9979 | 0.001-0.5 | 0.00013 | 0.00042 |
PB | y=1.85×102x+9.04×102 | 0.9981 | 0.005-0.5 | 0.00045 | 0.00150 |
2,4-D | y=7.74×102x+2.69×103 | 0.9998 | 0.001-0.5 | 0.00013 | 0.00042 |
MCPA | y=1.20×103x+1.44×103 | 0.9995 | 0.001-0.5 | 0.00010 | 0.00033 |
2,4,5-T | y=9.02×102x+2.87×103 | 0.9992 | 0.001-0.5 | 0.00015 | 0.00050 |
2,4-DB | y=2.77×102x+4.63×102 | 0.9999 | 0.005-0.5 | 0.00090 | 0.00300 |
2,4,5-TP | y=7.81×102x-5.87×102 | 0.9978 | 0.001-0.5 | 0.00015 | 0.00050 |
Analyte | Spiked/ (μg/L) | Recovery/ % | RSDs/% | Analyte | Spiked/ (μg/L) | Recovery/ % | RSDs/% | ||
---|---|---|---|---|---|---|---|---|---|
Intra-day | Inter-day | Intra-day | Inter-day | ||||||
4-CPA | 0.005 | 80 | 5.7 | 4.2 | 2,4,5-T | 0.005 | 88 | 4.7 | 6.0 |
0.05 | 89 | 2.4 | 7.3 | 0.05 | 92 | 2.9 | 10.7 | ||
0.2 | 92 | 1.4 | 5.6 | 0.2 | 89 | 4.7 | 6.0 | ||
PB | 0.005 | 81 | 8.8 | 7.2 | 2,4-DB` | 0.005 | 81 | 8.9 | 12.3 |
0.05 | 93 | 4.4 | 6.0 | 0.05 | 85 | 7.9 | 12.6 | ||
0.2 | 91 | 3.9 | 4.9 | 0.2 | 82 | 8.0 | 9.8 | ||
2,4-D | 0.005 | 81 | 7.4 | 9.8 | 2,4,5-TP | 0.005 | 102 | 9.4 | 10.8 |
0.05 | 91 | 3.9 | 5.2 | 0.05 | 91 | 3.2 | 8.2 | ||
0.2 | 89 | 3.1 | 4.6 | 0.2 | 88 | 3.1 | 8.2 | ||
MCPA | 0.005 | 91 | 7.0 | 5.2 | |||||
0.05 | 92 | 3.0 | 7.3 | ||||||
0.2 | 84 | 2.8 | 5.1 |
Table 3 Recoveries and precisions of the seven phenoxy acid herbicides (n=5)
Analyte | Spiked/ (μg/L) | Recovery/ % | RSDs/% | Analyte | Spiked/ (μg/L) | Recovery/ % | RSDs/% | ||
---|---|---|---|---|---|---|---|---|---|
Intra-day | Inter-day | Intra-day | Inter-day | ||||||
4-CPA | 0.005 | 80 | 5.7 | 4.2 | 2,4,5-T | 0.005 | 88 | 4.7 | 6.0 |
0.05 | 89 | 2.4 | 7.3 | 0.05 | 92 | 2.9 | 10.7 | ||
0.2 | 92 | 1.4 | 5.6 | 0.2 | 89 | 4.7 | 6.0 | ||
PB | 0.005 | 81 | 8.8 | 7.2 | 2,4-DB` | 0.005 | 81 | 8.9 | 12.3 |
0.05 | 93 | 4.4 | 6.0 | 0.05 | 85 | 7.9 | 12.6 | ||
0.2 | 91 | 3.9 | 4.9 | 0.2 | 82 | 8.0 | 9.8 | ||
2,4-D | 0.005 | 81 | 7.4 | 9.8 | 2,4,5-TP | 0.005 | 102 | 9.4 | 10.8 |
0.05 | 91 | 3.9 | 5.2 | 0.05 | 91 | 3.2 | 8.2 | ||
0.2 | 89 | 3.1 | 4.6 | 0.2 | 88 | 3.1 | 8.2 | ||
MCPA | 0.005 | 91 | 7.0 | 5.2 | |||||
0.05 | 92 | 3.0 | 7.3 | ||||||
0.2 | 84 | 2.8 | 5.1 |
Analyte | Spiked/(μg/L) | Tap water | Reservoir water | |||||
---|---|---|---|---|---|---|---|---|
Found/(μg/L) | Recovery/% | RSD/% | Found/(μg/L) | Recovery/% | RSD/% | |||
4-CPA | 0 | ND | ND | |||||
0.01 | 0.008 | 80 | 3.5 | 0.007 | 72 | 4.1 | ||
0.05 | 0.043 | 86 | 0.6 | 0.046 | 92 | 2.6 | ||
0.2 | 0.178 | 89 | 8.3 | 0.171 | 86 | 4.9 | ||
PB | 0 | ND | ND | |||||
0.01 | 0.009 | 90 | 5.5 | 0.008 | 80 | 2.4 | ||
0.05 | 0.044 | 88 | 2.3 | 0.045 | 90 | 4.1 | ||
0.2 | 0.182 | 91 | 2.5 | 0.179 | 90 | 6.5 | ||
2,4-D | 0 | ND | ND | |||||
0.01 | 0.008 | 80 | 11.3 | 0.009 | 90 | 7.6 | ||
0.05 | 0.042 | 84 | 3.1 | 0.047 | 94 | 2.9 | ||
0.2 | 0.179 | 90 | 2.3 | 0.168 | 84 | 1.5 | ||
MCPA | 0 | ND | ND | |||||
0.01 | 0.008 | 80 | 9.5 | 0.009 | 90 | 5.4 | ||
0.05 | 0.043 | 86 | 2.8 | 0.043 | 86 | 3.3 | ||
0.2 | 0.167 | 84 | 4.4 | 0.158 | 79 | 4.2 | ||
2,4,5-T | 0 | ND | ND | |||||
0.01 | 0.008 | 80 | 8.1 | 0.008 | 80 | 11.5 | ||
0.05 | 0.046 | 92 | 2.4 | 0.045 | 90 | 3.2 | ||
0.2 | 0.175 | 88 | 4.6 | 0.178 | 89 | 5.1 | ||
2,4-DB` | 0 | ND | ND | |||||
0.01 | 0.010 | 102 | 6.2 | 0.011 | 110 | 7.5 | ||
0.05 | 0.045 | 90 | 6.4 | 0.063 | 126 | 10.4 | ||
0.2 | 0.166 | 83 | 9.6 | 0.214 | 107 | 6.6 | ||
2,4,5-TP | 0 | ND | 0.004 | |||||
0.01 | 0.009 | 90 | 0.7 | 0.013 | 90 | 11.0 | ||
0.05 | 0.047 | 94 | 8.1 | 0.047 | 86 | 9.1 | ||
0.2 | 0.176 | 88 | 3.3 | 0.153 | 75 | 6.0 |
Table 4 Analytical results of the seven phenoxy acid herbicides in real water samples (n=3)
Analyte | Spiked/(μg/L) | Tap water | Reservoir water | |||||
---|---|---|---|---|---|---|---|---|
Found/(μg/L) | Recovery/% | RSD/% | Found/(μg/L) | Recovery/% | RSD/% | |||
4-CPA | 0 | ND | ND | |||||
0.01 | 0.008 | 80 | 3.5 | 0.007 | 72 | 4.1 | ||
0.05 | 0.043 | 86 | 0.6 | 0.046 | 92 | 2.6 | ||
0.2 | 0.178 | 89 | 8.3 | 0.171 | 86 | 4.9 | ||
PB | 0 | ND | ND | |||||
0.01 | 0.009 | 90 | 5.5 | 0.008 | 80 | 2.4 | ||
0.05 | 0.044 | 88 | 2.3 | 0.045 | 90 | 4.1 | ||
0.2 | 0.182 | 91 | 2.5 | 0.179 | 90 | 6.5 | ||
2,4-D | 0 | ND | ND | |||||
0.01 | 0.008 | 80 | 11.3 | 0.009 | 90 | 7.6 | ||
0.05 | 0.042 | 84 | 3.1 | 0.047 | 94 | 2.9 | ||
0.2 | 0.179 | 90 | 2.3 | 0.168 | 84 | 1.5 | ||
MCPA | 0 | ND | ND | |||||
0.01 | 0.008 | 80 | 9.5 | 0.009 | 90 | 5.4 | ||
0.05 | 0.043 | 86 | 2.8 | 0.043 | 86 | 3.3 | ||
0.2 | 0.167 | 84 | 4.4 | 0.158 | 79 | 4.2 | ||
2,4,5-T | 0 | ND | ND | |||||
0.01 | 0.008 | 80 | 8.1 | 0.008 | 80 | 11.5 | ||
0.05 | 0.046 | 92 | 2.4 | 0.045 | 90 | 3.2 | ||
0.2 | 0.175 | 88 | 4.6 | 0.178 | 89 | 5.1 | ||
2,4-DB` | 0 | ND | ND | |||||
0.01 | 0.010 | 102 | 6.2 | 0.011 | 110 | 7.5 | ||
0.05 | 0.045 | 90 | 6.4 | 0.063 | 126 | 10.4 | ||
0.2 | 0.166 | 83 | 9.6 | 0.214 | 107 | 6.6 | ||
2,4,5-TP | 0 | ND | 0.004 | |||||
0.01 | 0.009 | 90 | 0.7 | 0.013 | 90 | 11.0 | ||
0.05 | 0.047 | 94 | 8.1 | 0.047 | 86 | 9.1 | ||
0.2 | 0.176 | 88 | 3.3 | 0.153 | 75 | 6.0 |
Material | Method | Number of analytes | Matrices | Practicable pH | LOD/(μg/L) | Ref. |
---|---|---|---|---|---|---|
NH2-MWCNTs | MSPE-UPLC-MS/MS | 7 | lake, river, farmland and tap water | 5.4 | 0.01000-0.02000 | [12] |
PP-CMPs | DSPE-LC-MS/MS | 5 | tap, spring and pond water | 3 | 0.00055-0.00384 | [13] |
UiO-66-NM-PVDF MMM | DME-UPLC-MS/MS | 6 | sewage and reservoir water | 3-6 | 0.00003-0.00059 | [24] |
V-g-C3N4 | DSPE-DART-MS | 3 | tap and lake water | 2 | 0.00050-0.00200 | [28] |
MIL-101 | DSPE-UPLC-MS/MS | 12 | river water | 6 | 0.00018-0.00088 | [29] |
MIL-101-NM-PVDF MMM | DSPE-UPLC-MS/MS | 7 | tap and reservoir water | 6-7 | 0.00010-0.00090 | this work |
Table 5 Comparison of the present method with the reported methods for the determination of phenoxy acid herbicides
Material | Method | Number of analytes | Matrices | Practicable pH | LOD/(μg/L) | Ref. |
---|---|---|---|---|---|---|
NH2-MWCNTs | MSPE-UPLC-MS/MS | 7 | lake, river, farmland and tap water | 5.4 | 0.01000-0.02000 | [12] |
PP-CMPs | DSPE-LC-MS/MS | 5 | tap, spring and pond water | 3 | 0.00055-0.00384 | [13] |
UiO-66-NM-PVDF MMM | DME-UPLC-MS/MS | 6 | sewage and reservoir water | 3-6 | 0.00003-0.00059 | [24] |
V-g-C3N4 | DSPE-DART-MS | 3 | tap and lake water | 2 | 0.00050-0.00200 | [28] |
MIL-101 | DSPE-UPLC-MS/MS | 12 | river water | 6 | 0.00018-0.00088 | [29] |
MIL-101-NM-PVDF MMM | DSPE-UPLC-MS/MS | 7 | tap and reservoir water | 6-7 | 0.00010-0.00090 | this work |
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