Chinese Journal of Chromatography ›› 2020, Vol. 38 ›› Issue (3): 332-340.DOI: 10.3724/SP.J.1123.2019.10036
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ZHANG Wenmin2, FENG Zunmei2, HUANG Chuanhui2, GAO Jia1, ZHANG Lan1,2,*()
Received:
2019-10-31
Online:
2020-03-08
Published:
2020-12-10
Contact:
ZHANG Lan
Supported by:
ZHANG Wenmin, FENG Zunmei, HUANG Chuanhui, GAO Jia, ZHANG Lan. In-situ solvothermal polymerization of metal-organic framework/carbon-nitrogen nanosheet-coated solid-phase microextraction fiber for highly sensitive detection of pesticide residues in black tea[J]. Chinese Journal of Chromatography, 2020, 38(3): 332-340.
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URL: https://www.chrom-china.com/EN/10.3724/SP.J.1123.2019.10036
Compound | Retention time/min | Quantitative ion (m/z) | Qualitative ions (m/z) |
Heptachlor (七氯) | 13.92 | 272 | 273, 272, 237 |
Aldrin (艾试剂) | 14.82 | 263 | 263, 255, 220 |
Heptachlor epoxide | 15.98 | 263 | 353, 263, 193 |
(环氧七氯) | |||
α-Chlordane (α-氯丹) | 17.01 | 373 | 375, 373, 272 |
p, p′-DDE (p, p′-滴滴伊) | 17.63 | 318 | 318, 246, 176 |
α-Endosulfan (α-硫丹) | 18.64 | 241 | 241, 206, 195 |
p, p′-DDD (p, p′-滴滴滴) | 18.92 | 235 | 235, 200, 165 |
p, p′-DDT (p, p′-滴滴涕) | 20.10 | 235 | 235, 200, 165 |
Bifenthrin (联苯菊酯) | 21.91 | 181 | 386, 241, 181 |
Table 1 Retention times, quantitative ions and qualitative ions for the nine pesticides
Compound | Retention time/min | Quantitative ion (m/z) | Qualitative ions (m/z) |
Heptachlor (七氯) | 13.92 | 272 | 273, 272, 237 |
Aldrin (艾试剂) | 14.82 | 263 | 263, 255, 220 |
Heptachlor epoxide | 15.98 | 263 | 353, 263, 193 |
(环氧七氯) | |||
α-Chlordane (α-氯丹) | 17.01 | 373 | 375, 373, 272 |
p, p′-DDE (p, p′-滴滴伊) | 17.63 | 318 | 318, 246, 176 |
α-Endosulfan (α-硫丹) | 18.64 | 241 | 241, 206, 195 |
p, p′-DDD (p, p′-滴滴滴) | 18.92 | 235 | 235, 200, 165 |
p, p′-DDT (p, p′-滴滴涕) | 20.10 | 235 | 235, 200, 165 |
Bifenthrin (联苯菊酯) | 21.91 | 181 | 386, 241, 181 |
Fig. 1 Extraction performance of UiO-66/HOCN composite materials with various contents of HOCN for the nine pesticides (n=3) Experimental conditions: pesticide concentration, 100.0 ng/L; extraction temperature, 50 ℃; extraction time, 40 min; stirring rate, 500 r/min; desorption temperature, 280 ℃; desorption time, 5 min.
Fig. 2 (a) Transmission electron microscopy (TEM) image, (b) X-ray diffraction (XRD) pattern, (c) N2 adsorption-desorption isotherms, and (d) pore size distribution of UiO-66/HOCN composite materials
Fig. 4 Effects of (a) extraction temperature, (b) extraction time and (c) agitation speed on extraction efficiency of the nine pesticides (n=3) Experimental conditions were the same as those in Fig. 1. When one of the factors was investigated, all other factors remain the same.
Fig. 5 Effects of (a) desorption temperature and (b) desorption time on extraction efficiency of the nine pesticides (n=3) Experimental conditions were the same as those in Fig. 1. When one of the factors was investigated, all other factors remain the same.
Compound | Linear range/(ng/L) | R | LOD/(ng/L) | RSDs/% (n=3) | ||
Single fiber | Fibers of batch-to-batch | |||||
Intra-day | Inter-day | |||||
Heptachlor | 0.3-300.0 | 0.9996 | 0.1 | 4.9 | 6.8 | 7.2 |
Aldrin | 0.3-500.0 | 0.9997 | 0.1 | 4.5 | 4.5 | 6.2 |
Heptachlor epoxide | 0.3-300.0 | 0.9989 | 0.1 | 7.5 | 8.9 | 9.0 |
α-Chlordane | 0.5-300.0 | 0.9986 | 0.3 | 5.1 | 7.9 | 9.2 |
p, p′-DDE | 0.3-500.0 | 0.9978 | 0.1 | 4.5 | 8.2 | 8.3 |
α-Endosulfan | 0.3-800.0 | 0.9999 | 0.1 | 4.2 | 4.7 | 5.2 |
p, p′-DDD | 0.1-300.0 | 0.9999 | 0.03 | 4.3 | 6.4 | 7.8 |
p, p′-DDT | 0.1-300.0 | 0.9999 | 0.03 | 5.4 | 6.5 | 8.4 |
Bifenthrin | 0.8-500.0 | 0.9990 | 0.3 | 3.3 | 7.4 | 9.7 |
Table 2 Linear ranges, correlation coefficients (R), limits of detection (LODs), and precision of the proposed method
Compound | Linear range/(ng/L) | R | LOD/(ng/L) | RSDs/% (n=3) | ||
Single fiber | Fibers of batch-to-batch | |||||
Intra-day | Inter-day | |||||
Heptachlor | 0.3-300.0 | 0.9996 | 0.1 | 4.9 | 6.8 | 7.2 |
Aldrin | 0.3-500.0 | 0.9997 | 0.1 | 4.5 | 4.5 | 6.2 |
Heptachlor epoxide | 0.3-300.0 | 0.9989 | 0.1 | 7.5 | 8.9 | 9.0 |
α-Chlordane | 0.5-300.0 | 0.9986 | 0.3 | 5.1 | 7.9 | 9.2 |
p, p′-DDE | 0.3-500.0 | 0.9978 | 0.1 | 4.5 | 8.2 | 8.3 |
α-Endosulfan | 0.3-800.0 | 0.9999 | 0.1 | 4.2 | 4.7 | 5.2 |
p, p′-DDD | 0.1-300.0 | 0.9999 | 0.03 | 4.3 | 6.4 | 7.8 |
p, p′-DDT | 0.1-300.0 | 0.9999 | 0.03 | 5.4 | 6.5 | 8.4 |
Bifenthrin | 0.8-500.0 | 0.9990 | 0.3 | 3.3 | 7.4 | 9.7 |
Coating material | Linear range/(μg/L) | R | LODs/(ng/L) | RSDs/% | Ref. |
PDMS: polydimethylsiloxane; DVB: divinylbenzene; CAR: carboxen; PEG: polyethylene glycol. | |||||
UiO-66/HOCN | 0.1×10-3-0.8 | 0.9978-0.9999 | 0.03-0.30 | 3.3-9.7 | this study |
ZnO/g-C3N4 | 0.3×10-2-5.0 | 0.9981-0.9993 | 1.0-2.5 | 2.3-11.3 | [ |
PDMS | 0.1-500 | 0.9906-0.9988 | 40-410 | 3.2-11.3 | [ |
PDMS/DVB | 0.5-100 | 0.9901-0.9999 | 3-560 | <15 | [ |
DVB/CAR/PDMS | 1-100 | 0.9755-0.9997 | 200-400 | 7.2-24.6 | [ |
PEG | - | 0.9930-0.9990 | 3-145 | 4.2-10.0 | [ |
Table 3 Comparison of the proposed method with other reported methods
Coating material | Linear range/(μg/L) | R | LODs/(ng/L) | RSDs/% | Ref. |
PDMS: polydimethylsiloxane; DVB: divinylbenzene; CAR: carboxen; PEG: polyethylene glycol. | |||||
UiO-66/HOCN | 0.1×10-3-0.8 | 0.9978-0.9999 | 0.03-0.30 | 3.3-9.7 | this study |
ZnO/g-C3N4 | 0.3×10-2-5.0 | 0.9981-0.9993 | 1.0-2.5 | 2.3-11.3 | [ |
PDMS | 0.1-500 | 0.9906-0.9988 | 40-410 | 3.2-11.3 | [ |
PDMS/DVB | 0.5-100 | 0.9901-0.9999 | 3-560 | <15 | [ |
DVB/CAR/PDMS | 1-100 | 0.9755-0.9997 | 200-400 | 7.2-24.6 | [ |
PEG | - | 0.9930-0.9990 | 3-145 | 4.2-10.0 | [ |
Compound | Background/(ng/L)(RSD/%) | Recoveries (RSDs) at three spiked levels/% | ||
8 ng/L | 30 ng/L | 100 ng/L | ||
* Not detected. | ||||
Heptachlor | n. d.* | 82.9 (6.1) | 87.5 (3.6) | 94.9 (4.9) |
Aldrin | 6.6 (5.7) | 92.9 (7.6) | 98.1 (5.2) | 98.8 (7.8) |
Heptachlor epoxide | n. d.* | 111.2 (5.2) | 109.5 (8.5) | 87.4 (7.5) |
α-Chlordane | n. d.* | 103.4 (2.5) | 100.3 (4.3) | 97.6 (6.3) |
p, p′-DDE | n. d.* | 90.2 (7.1) | 94.3 (5.6) | 99.5 (4.3) |
α-Endosulfan | 54.7 (6.3) | 93.2 (4.1) | 98.5 (4.2) | 111.0 (3.7) |
p, p′-DDD | n. d.* | 85.5 (3.5) | 89.4 (7.3) | 105.0 (8.9) |
p, p′-DDT | n. d.* | 92.4 (4.0) | 90.2 (3.9) | 106.0 (6.4) |
Bifenthrin | 185.8 (2.5) | 102.8 (3.5) | 106.1 (4.7) | 117.0 (4.7) |
Table 4 Recoveries and RSDs of the nine pesticides spiked in a black tea sample (n=3)
Compound | Background/(ng/L)(RSD/%) | Recoveries (RSDs) at three spiked levels/% | ||
8 ng/L | 30 ng/L | 100 ng/L | ||
* Not detected. | ||||
Heptachlor | n. d.* | 82.9 (6.1) | 87.5 (3.6) | 94.9 (4.9) |
Aldrin | 6.6 (5.7) | 92.9 (7.6) | 98.1 (5.2) | 98.8 (7.8) |
Heptachlor epoxide | n. d.* | 111.2 (5.2) | 109.5 (8.5) | 87.4 (7.5) |
α-Chlordane | n. d.* | 103.4 (2.5) | 100.3 (4.3) | 97.6 (6.3) |
p, p′-DDE | n. d.* | 90.2 (7.1) | 94.3 (5.6) | 99.5 (4.3) |
α-Endosulfan | 54.7 (6.3) | 93.2 (4.1) | 98.5 (4.2) | 111.0 (3.7) |
p, p′-DDD | n. d.* | 85.5 (3.5) | 89.4 (7.3) | 105.0 (8.9) |
p, p′-DDT | n. d.* | 92.4 (4.0) | 90.2 (3.9) | 106.0 (6.4) |
Bifenthrin | 185.8 (2.5) | 102.8 (3.5) | 106.1 (4.7) | 117.0 (4.7) |
Fig. 6 Chromatograms of a black tea sample and a black tea sample spiked with standards Experimental conditions were the same as those in Fig. 1. Spiked level: 30 ng/L of each of the nine pesticides. Peak identifications: 1. heptachlor; 2. aldrin; 3. heptachlor epoxide; 4. α-chlordane; 5. p, p′-DDE; 6. α-endosulfan; 7. p, p′-DDD; 8. p, p′-DDT; 9. bifenthrin.
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