期刊论文详细信息
Journal of Environmental Health Science Engineering
Application of molecular imprinted polymer nanoparticles as a selective solid phase extraction for preconcentration and trace determination of 2,4-dichlorophenoxyacetic acid in the human urine and different water samples
Seyed Jamaleddin Shahtaheri1  Alireza Sedighi2  Hamid Sadeghi Abandansari3  Mohammad Behbahani3  Fariborz Omidi4 
[1] Department of Occupational Health Engineering, School of Public Health and Institute for Environmental Research, Tehran University of Medical Sciences, Tehran, Iran;Department of Occupational Health, School of Public Health, Tehran University of Medical Sciences, Tehran, Iran;Department of Chemistry, Shahid Beheshti University, Tehran, Iran;Department of Occupational Health Engineering, School of Public Health, Shahroud University of Medical Sciences, Shahroud, Iran
关键词: Urine and water samples;    Selective preconcentration;    2,4-dichlorophenoxyacetic acid;    Molecular imprinted polymer nanoparticles;   
Others  :  1175283
DOI  :  10.1186/s40201-014-0137-z
 received in 2013-12-25, accepted in 2014-10-29,  发布年份 2014
PDF
【 摘 要 】

A molecular-imprinted polymer nanoparticles (MIP-NP) for the selective preconcentration of 2,4-dichlorophenoxyacetic acid (2,4-D) is described. It was obtained by precipitation polymerization from methacrylic acid (the functional monomer), ethylene glycol dimethacrylate (the cross-linker), 2,2?-azobisisobutyronitrile (the initiator) and 2,4-D (the template molecule) in acetonitrile solution. The MIP-NPs were characterized by thermogravimetric analysis, and by scanning electron microscopy. Imprinted 2,4-D molecules were removed from the polymeric structure using acetic acid in methanol (15:85 v/v %) as the eluting solvent. The sorption and desorption process occur within 10 min and 15 min, respectively. The maximum sorbent capacity of the molecular imprinted polymer is 89.2 mg g?1. The relative standard deviation and limit of detection for water samples by introduced selective solid phase extraction were 4.2% and 1.25 ?g L?1, and these data for urine samples were 4.7% and 1.80 ?g L?1, respectively. The method was applied to the determination of 2,4-D in the urine and different water samples.

【 授权许可】

   
2014 Omidi et al.; licensee BioMed Central Ltd.; licensee BioMed Central Ltd.

【 预 览 】
附件列表
Files Size Format View
20150427100627922.pdf 1475KB PDF download
Figure 7. 48KB Image download
Figure 6. 31KB Image download
Figure 5. 10KB Image download
Figure 4. 69KB Image download
Figure 3. 9KB Image download
Figure 2. 53KB Image download
Figure 1. 46KB Image download
【 图 表 】

Figure 1.

Figure 2.

Figure 3.

Figure 4.

Figure 5.

Figure 6.

Figure 7.

【 参考文献 】
  • [1]Garabrant DH, Philbert MA: Review of 2, 4-dichlorophenoxyacetic acid (2, 4-D) epidemiology and toxicology. CRC Crit Rev Toxicol 2002, 32(4):233-257.
  • [2]Chaudhary AJ, M-u H, Grimes SM: Simultaneous recovery of metals and degradation of organic species: copper and 2, 4, 5-trichlorophenoxyacetic acid (2, 4, 5-T). J Hazard Mater 2009, 165(1):825-831.
  • [3]de Lipthay JR, Sørensen SR, Aamand J: Effect of herbicide concentration and organic and inorganic nutrient amendment on the mineralization of mecoprop, 2, 4-D and 2, 4, 5-T in soil and aquifer samples. Environ Pollut 2007, 148(1):83-93.
  • [4][http://www-cie.iarc.fr] webcite IARC: IARC monographs on the evaluation of carcinogenic risksto humans: chlorophenoxy herbicides. 1998, available on line .
  • [5]Reregistration Eligibility Decision for 2,4-D. EPA 738-R-05-002. 2005.
  • [6]Kohli J, Khanna R, Gupta B, Dhar M, Tandon J, Sircar K: Absorption and excretion of 2, 4-dichlorophenoxyacetic acid in man. Xenobiotica 1974, 4(2):97-100.
  • [7]Sauerhoff M, Braun W, Blau G, Gehring P: The fate of 2, 4-dichlorophenoxyacetic acid (2, 4-D) following oral administration to man. Toxicology 1977, 8(1):3-11.
  • [8]Toxicology of the Blood and Bone Marrow. Raven Press, New York; 1985.
  • [9]Harris S, Solomon K, Stephenson G: Exposure of homeowners and bystanders to 2, 4-dichlorophenoxyacetic acid (2, 4-D). J Environ Sci Health B 1992, 27(1):23-38.
  • [10]National Primary Drinking Water Regulations, Office of Water, U.S. Environmental Protection Agency, Washington, DC.; 2009.
  • [11]Hamilton D, Ambrus A, Dieterle R, Felsot A, Harris C, Holland P, Katayama A, Kurihara N, Linders J, Unsworth J, Wong S: Regulatory limits for pesticide residues in water (IUPAC Technical Report). Pure Appl Chem 2003, 75(8):1123-1155.
  • [12]Rodríguez I, Rubí E, González R, Quintana JB, Cela R: On-fibre silylation following solid-phase microextraction for the determination of acidic herbicides in water samples by gas chromatography. Anal Chim Acta 2005, 537(1¿2):259-266.
  • [13]Biesaga M, Jankowska A, Pyrzy?ska K: Comparison of different sorbents for solid-phase extraction of phenoxyalkanoic acid herbicides. Microchim Acta 2005, 150(3¿4):317-322.
  • [14]Catalina MI, Dallüge J, Vreuls RJ, Brinkman UAT: Determination of chlorophenoxy acid herbicides in water by in situ esterification followed by in-vial liquid¿liquid extraction combined with large-volume on-column injection and gas chromatography¿mass spectrometry. J Chromatogr A 2000, 877(1):153-166.
  • [15]Jing T, Wang Y, Dai Q, Xia H, Niu J, Hao Q, Mei S, Zhou Y: Preparation of mixed-templates molecularly imprinted polymers and investigation of the recognition ability for tetracycline antibiotics. Biosens Bioelectron 2010, 25(10):2218-2224.
  • [16]Behbahani M, Salarian M, Bagheri A, Tabani H, Omidi F, Fakhari A: Synthesis, characterization and analytical application of Zn (II)-imprinted polymer as an efficient solid-phase extraction technique for trace determination of zinc ions in food samples. J Food Compos Anal 2014, 34:81-89.
  • [17]Hoshina K, Horiyama S, Matsunaga H, Haginaka J: Molecularly imprinted polymers for simultaneous determination of antiepileptics in river water samples by liquid chromatography¿tandem mass spectrometry. J Chromatogr A 2009, 1216(25):4957-4962.
  • [18]Behbahani M, Barati M, Bojdi MK, Pourali AR, Bagheri A, Tapeh NAG: A nanosized cadmium (II)-imprinted polymer for use in selective trace determination of cadmium in complex matrices. Microchim Acta 2013, 180(11¿12):1117-1125.
  • [19]Prieto A, Schrader S, Bauer C, Möder M: Synthesis of a molecularly imprinted polymer and its application for microextraction by packed sorbent for the determination of fluoroquinolone related compounds in water. Anal Chim Acta 2011, 685(2):146-152.
  • [20]Lucci P, Núñez O, Galceran MT: Solid-phase extraction using molecularly imprinted polymer for selective extraction of natural and synthetic estrogens from aqueous samples. J Chromatogr A 2011, 1218(30):4828-4833.
  • [21]Behbahani M, Bagheri S, Amini MM, Sadeghi Abandansari H, Moazami HR, Bagheri A: Application of a magnetic molecularly imprinted polymer for the selective extraction and trace detection of lamotrigine in urine and plasma samples. J Sep Sci 2014, 37:1610-1616.
  • [22]Shahtaheri S, Katmeh M, Kwasowski P, Stevenson D: Development and optimisation of an immunoaffinity-based solid-phase extraction for chlortoluron. J Chromatogr A 1995, 697(1):131-136.
  • [23]Koohpaei A, Shahtaheri S, Ganjali M, Forushani AR, Golbabaei F: Application of multivariate analysis to the screening of molecularly imprinted polymers (MIPs) for ametryn. Talanta 2008, 75(4):978-986.
  • [24]Koohpaei A, Shahtaheri S, Ganjali M, Forushani AR, Golbabaei F: Optimization of solid-phase extraction using developed modern sorbent for trace determination of ametryn in environmental matrices. J Hazard Mater 2009, 170(2):1247-1255.
  • [25]Bulut VN, Gundogdu A, Duran C, Senturk HB, Soylak M, Elci L, Tufekci M: A multi-element solid-phase extraction method for trace metals determination in environmental samples on Amberlite XAD-2000. J Hazard Mater 2007, 146(1¿2):155-163.
  • [26]Soylak M, Ercan O: Selective separation and preconcentration of copper (II) in environmental samples by the solid phase extraction on multi-walled carbon nanotubes. J Hazard Mater 2009, 168(2¿3):1527-1531.
  • [27]Ebrahimzadeh H, Behbahani M: A novel lead imprinted polymer as the selective solid phase for extraction and trace detection of lead ions by flame atomic absorption spectrophotometry: synthesis, characterization and analytical application.Arab J CHEM 2013, doi:10.1016/j.arabjc.2013.09.017.
  • [28]Omidi F, Behbahani M, Samadi S, Sedighi A, Shahtaheri SJ: Coupling of molecular imprinted polymer nanoparticles by high performance liquid chromatography as an efficient technique for sensitive and selective trace determination of 4-chloro-2-methylphenoxy acetic acid in complex matrices. Iranian J Publ Health 2014, 43(5):645-657.
  • [29]Wang T, Tong J, Sun M, Chen L: Fast and selective extraction of chloramphenicol from soil by matrix solid-phase dispersion using molecularly imprinted polymer as dispersant. J Sep Sci 2011, 34(15):1886-1892.
  • [30]Tamayo FG, Casillas JL, Martin-Esteban A: Highly selective fenuron-imprinted polymer with a homogeneous binding site distribution prepared by precipitation polymerisation and its application to the clean-up of fenuron in plant samples. Anal Chim Acta 2003, 482(2):165-173.
  • [31]Haginaka J, Sanbe H: Uniform-sized molecularly imprinted polymers for 2-arylpropionic acid derivatives selectively modified with hydrophilic external layer and their applications to direct serum injection analysis. Anal Chem 2000, 72(21):5206-5210.
  • [32]Turiel E, Martín-Esteban A, Tadeo JL: Molecular imprinting-based separation methods for selective analysis of fluoroquinolones in soils. J Chromatogr A 2007, 1172(2):97-104.
  • [33]He J, Lv R, Zhu J, Lu K: Selective solid-phase extraction of dibutyl phthalate from soybean milk using molecular imprinted polymers. Anal Chim Acta 2010, 661(2):215-221.
  • [34]Yan H, Qiao J, Pei Y, Long T, Ding W, Xie K: Molecularly imprinted solid-phase extraction coupled to liquid chromatography for determination of Sudan dyes in preserved beancurds. Food Chem 2012, 132(1):649-654.
  • [35]Djozan D, Ebrahimi B: Preparation of new solid phase micro extraction fiber on the basis of atrazine-molecular imprinted polymer: application for GC and GC/MS screening of triazine herbicides in water, rice and onion. Anal Chim Acta 2008, 616(2):152-159.
  • [36]Akiyama T, Hishiya T, Asanuma H, Komiyama M: Molecular imprinting of cyclodextrin on silica-gel support for the stationary phase of high-performance-liquid-chromatography. J Inclusion Phenom Macrocyclic Chem 2001, 41(1¿4):149-153.
  • [37]Zhang H, Dramou P, He H, Tan S, Pham-Huy C, Pan H: Molecularly imprinted stationary phase prepared by reverse micro-emulsion polymerization for selective recognition of gatifloxacin in aqueous media. J Chromatogr Sci 2012, 50(6):499-508.
  • [38]Kan X, Zhao Y, Geng Z, Wang Z, Zhu J-J: Composites of multiwalled carbon nanotubes and molecularly imprinted polymers for dopamine recognition. J Phys Chem C 2008, 112(13):4849-4854.
  • [39]Ye L, Mosbach K, Spivak DA, Sibrian-Vazquez M: Molecularly Imprinted Materials: Towards the Next Generation. Materials Research Society Symposium Proceedings. Cambridge Univ Press; 2002.
  • [40]Tokonami S, Shiigi H, Nagaoka T: Review: micro- and nanosized molecularly imprinted polymers for high-throughput analytical applications. Anal Chim Acta 2009, 641(1¿2):7-13.
  • [41]Haginaka J: Monodispersed, molecularly imprinted polymers as affinity-based chromatography media. J Chromatogr B 2008, 866(1¿2):3-13.
  • [42]Ye L, Cormack PA, Mosbach K: Molecularly imprinted monodisperse microspheres for competitive radioassay. Anal Commun 1999, 36(2):35-38.
  文献评价指标  
  下载次数:21次 浏览次数:5次