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第 9 期 李培英,等: 萃取非甾体抗炎药物材料的制备及性能 ·1787·
由表 5 可知,该方法对目标化合物的回收率在 non-steroidal anti-inflammatory drugs from waste water samples by
80%以上,SD≤5.1%,线性范围在 10~1000 μg/L,检 rotating-disk sorptive extraction[J].Talanta, 2014, 128: 486-492.
[10] United States Environmental Protection Agency. Determination of
出限和定量限分别为 0.02~0.10 μg/L 和 0.07~0.33 μg/L, pharmaceuticals and personal care products in drinking water by
低于文献报道的超支化大容量混合阴离子交换固相萃 solid phase extraction and liquid chromatography electrospray
取柱检出限(4~9 μg/L)和定量限(5~33 μg/L) [12] 。 ionization tandem mass spectrometry (LC/ESI-MS/MS): Method
542[S]. Washington, D.C: United States, 2016.
[11] WANG Y K, OU Y H, XIE S Y, et al. Magnetic graphene solid-phase
3 结论 extraction for the determination of 47 kinds of non-steroidal anti-
inflammatory drug residues in animal food with liquid chromatography
(1)本研究以 1,6-己二胺、乙二醛和甲醛为原 tandem mass spectrometry[J]. Food Analytical Methods, 2019, 12(6):
料、醋酸为阴离子、水为溶剂,60 ℃下成功制备了 1346-1368.
[12] HUANG C N, LI Y, YANG J J, et al. Hyperbranched mixed-mode
PAIL,且 PAIL 已成功涂覆在 Oxi-CFP 上,制备出 anion-exchange polymeric sorbent for highly selective extraction of
成本低廉的萃取纸。 nine acidic non-steroidal anti-inflammatory drugsfrom human urine[J].
(2)制备的萃取纸可用于水中 NSAIDs 的富集 Talanta, 2018, 190: 15-22.
[13] GILART N, MARCE R M, FONTANALS N, et al. A rapid
浓缩。当 PAIL 制备温度为 60 ℃时且 PAIL 的质量 determination of acidic pharmaceuticals in environmental waters by
分数为 5%时,制备的萃取纸对 4 种 NSAIDs 的吸附 molecularly imprinted solid-phase extraction coupled to tandem mass
2
2
量,分别为 80.4 ng/cm (托美汀)、76.3 ng/cm (酮 spectrometry without chromatography[J]. Talanta, 2013, 110: 196-201.
[14] DAHANE S, GARCIA M D G, BUENO M J M, et al. Determination
2
2
洛芬)、103.0 ng/cm (萘普生)、122.0 ng/cm (双 of drugs in river and wastewaters using solid-phase extraction by
氯芬酸)。 packed multi-walled carbon nanotubes and liquid
(3)建立了萃取纸与 HPLC-MS/MS 联用萃取 chromatography-quadrupole-linear ion trap-mass spectrometry[J].
Journal of Chromatography A, 2013, 1297: 17-28.
检测水中 4 种 NSAIDs 的方法,加标回收率均> [15] MASHKURAH A R, IBRAHIM W A W, RAMLI Z, et al. New
80%、检出限和定量限分别为 0.02~0.10 μg/L 和 sol-gel hybrid material in solid phase extraction combined with liquid
0.07~0.33 μg/L。 chromatography for the determination of non-steroidal anti-
inflammatory drugs in water samples[J]. Chromatographia, 2016,
79(7/8): 421-429.
参考文献:
[16] DUAN A Y (段安阳), LI Z Q (李柱泉), SU Y F (苏扬帆), et al.
[1] ZHANG Y J, GEISSEN S U, GAL C. Carbamazepine and diclofenac: Modification of cellulose nanofiber membrane and its adsorption
Removal in wastewater treatment plants and occurrence in water properties for dyes[J]. Fine Chemicals (精细化工), 2020, 37(10):
bodies[J]. Chemosphere, 2008, 73(8): 1151-1161. 2002-2008.
[2] GALLO P, FABBROCINO S, VINCI F, et al. Multi-residue [17] SARAJI M, FARAJMAND B. Chemically modified cellulose paper
determination of non-steroidal anti-inflammatory drug residues in as a thin film microextraction phase[J]. Journal of Chromatography
animal serum and plasma by HPLC and photo-diode array detection[J]. A, 2013, 1314: 24-30.
Journal of Chromatographic Science, 2006, 44(10): 585-590. [18] WANG X C (王学川), HAO D Y (郝东艳), JI L (季李), et al.
[3] EADES C, WARING C P. The effects of diclofenac on the physiology Synthesis of imidazole type ionic liquid amphoteric polymer and its
of the green shore crab carcinus maenas[J]. Marine Environmental application in fatliquoring[J]. Fine Chemicals (精细化工), 2020,
Research, 2010, 69(S1): S46-S48. 37(5): 1024-1031.
[4] WINKER M, FAIKA D, GULYAS H, et al. A comparison of human [19] AGUILERA-HERRADOR E, LUCENA R, CARDENAS S, et al.
pharmaceutical concentrations in raw municipal wastewater and The roles of ionic liquids in sorptive microextraction techniques[J].
yellowwater[J]. Science of the Total Environment, 2008, 399(1/2/3): Trac-Trends in Analytical Chemistry, 2010, 29(7): 602-616.
96-104. [20] ZHAO F, MENG Y J, ANDERSON J L. Polymeric ionic liquids as
[5] AL-RIFAI J H, KHABBAZ H, SCHAFER A I. Removal of selective coatings for the extraction of esters using solid-phase
pharmaceuticals and endocrine disrupting compounds in a water microextraction[J]. Journal of Chromatography A, 2008, 1208(1/2):
recycling process using reverse osmosis systems[J]. Separation and 1-9.
Purification Technology, 2011, 77(1): 60-67. [21] MENG Y J, PINO V N, ANDERSON J L. Exploiting the versatility
[6] RACAMONDE I, RODIL R, QUINTANA J B, et al. Fabric phase of ionic liquids in separation science: Determination of low-volatility
sorptive extraction: A new sorptive microextraction technique for the aliphatic hydrocarbons and fatty acid methyl esters using headspace
determination of non-steroidal anti-inflammatory drugs from solid-phase microextraction coupled to gas chromatography[J].
environmental water samples[J]. Analytica Chimica Acta, 2015, 865: Analytical Chemistry, 2009, 81(16): 7107-7112.
22-30. [22] LINDNER J P. Imidazolium-based polymers via the poly-
[7] OAKS J L, GILBERT M, VIRANI M Z, et al. Diclofenac residues as Radziszewski reaction[J]. Macromolecules, 2016, 49(6): 2046-2053.
the cause of vulture population decline in Pakistan[J]. Nature, 2004, [23] SAXER S, MARESTIN C, MERCIER R, et al. The multicomponent
427(6975): 630-633. Debus-Radziszewski reaction in macromolecular chemistry[J].
[8] BENDZ D, PAXEUS N A, GINN T, et al. Occurrence and fate of Polymer Chemistry, 2018, 9(15): 1927-1933.
pharmaceutically active compounds in the environment, a case study: [24] DAMILANO G, KALEBIC D, BINNEMANS K, et al. One-pot
Höje River in Sweden[J]. Journal of Hazardous Materials, 2005, synthesis of symmetric imidazolium ionic liquids N,N-disubstituted
122(3): 195-204. with long alkyl chains[J]. RSC Advances, 2020, 10(36): 21071-21081.
[9] MANZO V, HONDA L, NAVARRO O, et al. Microextraction of (下转第 1819 页)