Recognition Properties for Pyrrole

Recognition Properties for Pyrrole Preparation of molecularly imprinted polymer and its recognition properties for pyrrole X.W. Wu, J. Wang, H.X. Wang  [1], Q.M. Zhou, L.H. Liu. wang, Y.P. Wu, H.W. Yang, G.L. Zhao, S.X. Tuo Abstract: The molecularly-imprinted polymer (MIP) of pyrrole was synthesized by a precipitation polymerization method using acrylamide (AM) as functional monomer and ethylene glycol dimethacrylate (EGDMA) as cross-linker agent in acetonitrile. MIP of pyrrole was characterized by FT-IR and UV. The surface morphology and specific surface area of the MIP was characterized by Scanning Electron Microscope (SEM) and nitrogen adsorption (BET). The adsorption behavior of the MIP was investigated in detail, which showed high selectivity for pyrrole, the results indicated that the maximum binding capacities of pyrrole on the MIP and the non-imprinted polymer (NIP) were 404 and 265 ÃŽ ¼molΆ¡g−1, respectively. Application of MIP with a high selectivity to pyrrole provides a novel method for separating and purifying the trace nitrogenous heterocyclic compounds from tobacco. Keyword: molecularly imprinted polymer, pyrrole, tobacco, nitrogenous heterocyclic compounds 1 INTRODUCTION The Pyrrole and other nitrogenous heterocyclic compounds in tobacco leaves come mainly from the reaction products formed by the reaction of sugar and amino acid[1-3], which play an important role in sensory quality of tobacco and tobacco products. They are the important parameters to evaluate the sensory quality of tobacco products and have great effects on the sensory characteristics of tobacco products and on the health of smokers[4]. Therefore, the studies and analysis of nitrogenous heterocyclic compounds are conducive to improve the quality of perfuming and tobacco products. Molecular Imprinting, as an interdiscipline derived from polymer chemistry, material science, and biological chemistry, is the method of preparing the polymer with particular selection to given template molecules[5-8]. So far, dozens of countries, (i.e., America, Japan, Germany, Australia, France and China) hundreds of academic institutions and enterprises have been working on the research and development of the molecularly imprinted polymer (MIP).Thanks to MIP is simple in preparation and can be easily preserved, with specific selectivity, high temperature, high pressure and acid corrosion, it has been widely used in the solid phase extraction[9], chromatography analysis [10], membrane separation [11], biomimetic sensor[12], ect. The separation of bioactive ingredients in natural products is difficult because of their low contents, complex structures and diversity[13-15]. Compared with traditional methods (high performance liquid chromatography, silica gel column chromatography, etc.), molecular imprinting method has the advantages of high molecular recognition, simple operation, low solvent consumption and recyclable[16]. Thus, the molecularly imprinting technique has attracted considerable attention for extraction of compounds from complex mixtures of chemical species[17-18]. However, to the best of our knowledge, no molecularly imprinted polymer has been reported for the separation and determination of pyrrole in tobacco so far. In this study, pyrrole imprinted polymer was synthesized by employing acrylamide (AM) as functional monomer and ethylene glycol dimethacrylate (EGDMA) as crosslinking. After the characteristics and analysis of the MIP and NIP, the adsorption behavior including kinetics and isotherms are discussed in detail. It was found that the MIP can specifically adsorb and identify pyrrole molecules, which meant the MIP can be applied to separation and enrichment of trace pyrrole in tobacco. The aim of this paper is to provide theoretical basis and technical supports for further study of the effects of nitrogen heterocyclic compound on tobacco quality. 2 EXPERIMENTAL 2.1 Reagents Pyrrole, pyridine and methanol were obtained from Sinopharm Chemical Reagent Co., Ltd. (Shanghai, China). Acrylamide, methacrylic acid, acetonitrile and azodiisobutyronitrile were purchased from Tianjin Kermel Chemical Reagent Company (Tianjin, China). Ethylene glycol dimethacrylate was obtained from Aladdin reagent co., LTD (Guangdong, China). All the solvents were of analytical reagent grade and used without further purification. 2.2 Synthesis of MIP and NIP The pyrrole imprinted polymer was prepared by precipitation polymerization in the following procedures. 0.1 mmol of pyrrole and 0.4 mmol of AM were dissolved in 20 ml of acetonitrile in a 40 mL glass vessel. The mixture was sonicated at room temperature for 30 minutes for pre-polymerization, and then was incubated at 4à ¢Ã¢â‚¬Å¾Ã†â€™Ã‚ °C for 12 h. Subsequently, 2 mmol of cross-linker (EGDMA) and 10 mg of initiator (AIBN) were added stepwise. The glass vessel was degassed in a sonicating bath for 10 min, and filled with nitrogen for 30 min, and then sealed for polymerization at 60  °C for 24 h in a thermostat water bath. After polymerization, the resultants were extracted with a mixed solvent of methanol/acetic acid (9:1, v/v) for 48 h in a Soxhlet extractor to remove the template from its polymeric matrix, followed by ethanol for another 48 h to remove the acetic acid. The obtained MIP was dried in an oven at 60  °C overnight. As a control, the NIP was prepared and treated unde r identical conditions except for the omission of the template. 2.3 Morphological characterization The FT-IR spectra were recorded to characterize the MIP and NIP on an AVATAR 360 ESP FT-IR spectrometer (Nicolet, America). SEM images were obtained with afield-emission scanning electron microscope (FE-SEM, JSM-6700F, JEOL, Japan). The nitrogen adsorption/desorption data of MIP and NIP was determined using an ASAP2020Micromeriticsapparatus (Micromeritics Instruments, USA). 2.4 Binding experiments The binding experiments were carried out at 30  °C and 150 rpm on an orbital shaker with 100 mg of the MIP and NIP in a 100 mL flask containing pyrrole in 20 ml of acetonitrile. Batch experiments were performed to examine the adsorption kinetics and equilibrium. In the kinetic adsorption experiments, 2.5 mmolΆ¡L-1 pyrrole in acetonitrile was used. The adsorption isotherm experiments were conducted with the initial pyrrole concentration ranging from 0.2 to 5.0 mmolΆ¡L-1 for 2 h. After the adsorption, the concentration of the substrates in the supernatant solutions was determined via an UV-2450 Ultraviolet Spectrophotometer (Shimadzu, Japan). The binding capacity of pyrrole and the analogs was calculated from the equation: (1) Where: Q stands for the binding capacity (ÃŽ ¼molΆ¡g−1), C0 and C are the initial and the residual concentrations (mmolΆ¡L-1) of pyrrole, respectively, V is the solution volume (mL), and m is the amount (mg) of the MIP or NIP used for the adsorption experiments. 3 RESULTS AND DISCUSSION 3.1 Interaction between pyrrole and the functional monomers In order to investigate the feasibility of imprinted pyrrole, two different functional monomers MAA and AM were investigated for the formation of complex with the template. The maximum absorption wavelength of pyrrole was measured by the UV-2450 Ultraviolet Spectrophotometer. As shown in Fig.1, compared with MAA, AM demonstrated much stronger interaction with pyrrole for the non-existent absorbance of pyrrole. It is possible that the complex of pyrrole with AM was formed via hydrogen bonding between N–H of pyrrole and –CONH2 of AM due to the pre-polymerization. Fig.1 Interaction between pyrrole and functional monomers 3.2 The molar ratio of pyrrole to the monomer In order to elucidate the recognition mechanism on a molecular level, spectrophotometric analysis was employed in the pyrrole imprinting process. A series solution were prepared in acetonitrile, in which the molar ratio of pyrrole and AM varied at 1:0, 1:2, 1:4 and 1:6, respectively. After equilibrium for 12 h, absorption spectrums of the mixture were measured via an UV-2450 Ultraviolet Spectrophotometer. As shown in Fig.2, the absorbance decreased with the increasing concentration of AM, When the molar ratio of pyrrole and AM up to 1:4, the absorption peak of pyrrole disappeared, which indicated that the pyrrole had reacted with AM completely. While molar ratio of pyrrole and AM exceeded 1:4, the excess of AM could self-associate, and formed non-specific binding site, which makes the adsorption mass transfer resistance increase and is not conducive to the preparation of molecularly imprinted polymer. Therefore, the optimal molar ratio of pyrrole and AM is 1:4. Fig.2 Absorption spectra of pyrrole with different proportion of AM in acetonitrile 3.3 Characteristics of MIP and NIP 3.3.1 Characterisation of MIP and NIP by FT-IR spectra Pyrrole, AM, EGDMA, MIP (before and after eluting templates) and NIP were compared to affirm the successful preparation of MIP by FT-IR spectra. The FT-IR spectra of the MIP before and after removal of template pyrrole are presented in Fig.3a and Fig.3b, respectively. The –NH stretching vibration band of monomer AM (Fig.3e) appeared at 3580 cm-1 in the spectra of MIP before pyrrole removal (Fig.3a), which indicated that the template pyrrole formed hydrogen bonding interaction with monomer AM, this band is shifted to a higher wavenumber (at 3585 cm-1) after removal of pyrrole in MIP (Fig.3b). A conspicuous band at 1648 cm-1 in the spectra of MIP before removal of template pyrrole is ascribed to -C=C- aromatic ring stretching vibration of pyrrole (Fig.3d). This band disappeared after removal of pyrrole in MIP (Fig.3a) and was not observed in spectra of NIP (Fig.3c) due to absence of pyrrole. The peak at 3597cm-1 inFig.3c corresponds to the –NH stretching of monomer AM in the FT-IR spectra of NIP. The absorption peaks of MIP and NIP were similar, which means that both MIP after eluting templates and NIP have the same chemical components. Fig.3 IR spectra of (a) MIP before eluting template, (b) MIP after eluting template , (c) NIP, (d) pyrrole, (e) AM 3.3.2 Morphology of MIP and NIP The morphology of MIP and NIP was shown in Fig.4. As shown in Fig.4 (a), the prepared polymer is microsphere and the particle is uniform, which indicated the spherical particle can be synthesized at the best experiment condition. The MIP microsphere has a narrow and small particle size, and the average diameter is 2ÃŽ ¼m. As for NIP, the microsphere with a narrow but big particle size, and the average diameter is 3ÃŽ ¼m. Much imino exist in the template molecule, which may suppress the polymerization, results in the bigger particle size of NIP compared with MIP. Besides, the whole reaction system polarity increased with the added template molecule, the solubility of MIP decreased, so that MIP precipitated from the whole reaction system early, which can also generate the bigger particle size of NIP. Fig.4 SEM micrographs of (a) MIP, (b) NIP. 3.3.3 Characterization of specific surface area Table 1 lists the results of nitrogen adsorption experiments for MIP and NIP particles. It can be seen that the specific surface area and the average pore diameter were different for MIP and NIP particles. Table1 Structure parameters of MIP and NIP a Measured by Brunauer–Emmett–Teller (BET) method. b Measured by Barrett–Joyner–Halenda (BJH) method. 3.4 Binding performance of MIP and NIP 3.4.1 Absorption isotherms and kinetic of pyrrole on the MIP and NIP The absorption isotherm curves of pyrrole on the MIP and NIP were plotted in Fig.5. The absorption capacity was increased gradually with increasing initial concentration of pyrrole in the range of 0.2-5.0 mmol ·L−1. In the higher concentration range, the binding capacity was close to be stable. The binding data can be analyzed by Langmuir equation: (2) Where Q stands for the binding capacity (ÃŽ ¼molΆ¡g−1), Qmax is the maximum binding capacity (ÃŽ ¼molΆ¡g−1), Ceq is equilibrium concentration of pyrrole (mmol ·L−1), and B is a constant. In order to calculate the maximum binding capacity of pyrrole on both MIP and NIP, this equation was changed into Eq. (3): (3) Eq. (3) shows a linear relationship between Ceq/Q and Ceq. From the slope of the linear plot, the maximum binding capacities of pyrrole on the MIP and NIP were calculated to be 404 and 265 ÃŽ ¼molΆ¡g−1, respectively, which means that the maximum binding capacity of pyrrole on MIP was 1.52 times of that on NIP. In addition, under the same experimental conditions, the adsorption capacity of the MIP at each concentration was higher than that of the NIP. It was indicated that MIP offered a higher affinity for the template molecule than NIP. Fig.5 Adsorption isotherms of pyrrole on MIP and NIP 3.4.2 Binding kinetic curve of pyrrole pyrrole on the MIP As shown in Fig.6, the adsorption kinetic curves of pyrrole on MIP and MIP were shown at the pyrrole concentration of 2.5 mmol ·L−1 in acetonitrile. It can be seen that the binding capacity of MIP increased rapidly in the period of 0-60 min, and then the increments were reduced on the stage of 60-80 min, and the saturated binding was observed after 80 min. Fig.6 Adsorption kinetic curves of pyrrole on MIP and NIP 3.4.3 Selective adsorption In the selective adsorption test, the target molecule pyrrole and the competitive one pyridine possess similar structure and co-exist in tobacco extract as nitrogenous heterocyclic compounds. As we can see in Table 2, it is obvious that the absorption capacity of pyrrole and pyridine of MIP was much higher than that of the NIP. The selectivity of MIP was 2.17 times higher than that of NIP, which suggested that the imprinting process significantly improved adsorption selectivity to the template. Table 2 Binding capacity of different substrates on MIP and NIP 4 CONCLUSIONS In this paper, the pyrrole molecularly imprinted polymer was synthesized via the facile precipitation-polymerization method. The prepared polymer is microsphere and the diameter is about 2 ÃŽ ¼m. The binding property experiments indicated the imprinted polymer can adsorb the pyrrole molecule selectively. Moreover, the adsorb effect of MIP is stronger than NIP. The selective adsorption experiments demonstrated the synthesized MIP microsphere has the obvious selective adsorption effect with pyrrole molecule when compared the similar structure pyridine. This work provided theoretical basis for the new direction of separation and purification in the field of tobacco with pyrrole and other heterocyclic compounds. 5 ACKNOWLEDGEMENT This work was supported by China Tobacco Hunan Industrial Co., Ltd, Technology research and development center project (2011-JC-0001) REFERENCES Kulshreshtha, N. P., Moldoveanu, S. C. (2003). Analysis of pyridines in mainstream cigarette smoke. Journal of Chromatography A, 985(1), 303-312. Leffingwell, J. C., Alford, E. D. (2005). Volatile constituents of perique tobacco. Electronic Journal of Environmental, Agricultural and Food Chemistry, 4(2), 899-915. Duan, J., Huang, Y., Li, Z., Zheng, B., Li, Q., Xiong, Y., Min, S. (2012). Determination of 27 chemical constituents in Chinese southwest tobacco by FT-NIR spectroscopy. Industrial Crops and Products, 40, 21-26. YU, J. J., PANG, T. H., REN, X. H., LI, L., DAI, H. J., LI, A. J. (2006). Research on Relationship between Neutral Aroma Constituents and Smoking Quality in Flue-Cured Tobacco [J]. Journal of Henan Agricultural University, 4, 001. Mosbach, K. (1994). Molecular imprinting. Trends in biochemical sciences, 19(1), 9-14. Andersson, L. I. (2000). Molecular imprinting: developments and applications in the analytical chemistry field. Journal of Chromatography B: Biomedical Sciences and Applications, 745(1), 3-13. Bures, P., Huang, Y., Oral, E., Peppas, N. A. (2001). Surface modifications and molecular imprinting of polymers in medical and pharmaceutical applications. Journal of Controlled Release, 72(1), 25-33. Piletsky, S. A., Alcock, S., Turner, A. P. (2001). Molecular imprinting: at the edge of the third millennium. TRENDS in Biotechnology, 19(1), 9-12. Zhang, W., Chen, Z. (2013). Preparation of micropipette tip-based molecularly imprinted monolith for selective micro-solid phase extraction of berberine in plasma and urine samples. Talanta, 103, 103–109. Ebrahimzadeh, H., Dehghani, Z., Asgharinezhad, A. A., Shekari, N., Molaei, K. (2013). Determination of haloperidol in biological samples using molecular imprinted polymer nanoparticles followed by HPLC-DAD detection. International journal of pharmaceutics, 453(2), 601-609. Ulbricht, M. (2004). Membrane separations using molecularly imprinted polymers. Journal of chromatography B, 804(1), 113-125. Sergeyeva, T. A., Slinchenko, O. A., Gorbach, L. A., Matyushov, V. F., Brovko, O. O., Piletsky, S. A., Elska, G. V. (2010). Catalytic molecularly imprinted polymer membranes: Development of the biomimetic sensor for phenols detection. Analytica chimica acta, 659(1), 274-279. Colegate, S. M., Molyneux, R. J. (Eds.). (2007). Bioactive natural products: detection, isolation, and structural determination. CRC press. Mishra, B. B., Tiwari, V. K. (2011). Natural products: an evolving role in future drug discovery. European journal of medicinal chemistry, 46(10), 4769-4807. REN, Q., XING, H., BAO, Z., SU, B., YANG, Q., YANG, Y., ZHANG, Z. (2013). Recent Advances in Separation of Bioactive Natural Products. Chinese Journal of Chemical Engineering, 21(9), 937-952. Cheong, W. J., Yang, S. H., Ali, F. (2013). Molecular imprinted polymers for separation science: A review of reviews. Journal of separation science, 36(3), 609-628. Hu, Y., Pan, J., Zhang, K., Lian, H., Li, G. (2013). Novel applications of molecularly-imprinted polymers in sample preparation. TrAC Trends in Analytical Chemistry, 43, 37-52. Andersson, L. I. (2000). Molecular imprinting for drug bioanalysis: a review on the application of imprinted polymers to solid-phase extraction and binding assay. Journal of Chromatography B: Biomedical Sciences and Applications, 739(1), 163-173. 1 [1]E-mail:[emailprotected]; [emailprotected]; [emailprotected]

Female Serial Killers Essay -- essays research papers

Female Serial Killers While most of the violent crimes that happens most are them are belongs to men, women have not been the wilting flowers promoted so heartily by Victorian adorers and (right or wrong) often evident in today's society. Before we get into detail about the fascinating phenomenon of the Black Widow, it is worth a brief overview of women's escalating role in the world of violent crime, particularly in the United States. Since 1970, there has been an increasing and alarming rise 138 percent of violent crimes committed by women. Still, while the equivalent percentage compared to male violence is small 15 percent to 85 percent the fact that the numbers have elevated so drastically points to something changing in society. Sociologists try to explain it, so do criminologists, theologizes, politicians and world historians, but the resulting message is clear, and that message is that females are not alien to committing violent acts. In recent years, women have committed some of the most heinous crimes. Darlie Routier killed her two sons for reasons blamed on personal economics. Diane Downs killed one of her three children (she tried to kill all of them) in order to win back a lover who didn't want kids. Susan Smith drowned her boys in a neighborhood lake because her boyfriend did not want the responsibility of raising some other man's children. Karla Homolka and husband Paul Bernardo sexually assaulted, tortured and killed several young women for thrills. There a...

Local and Global Effects of Deforestation Essay

Trees are one of the most important aspects of the plant we live in. Trees are vitally important to the environment, animals and mostly us humans. So deforesting them will cause local and global effects on the environment and therefore harming us as well. They are also important for the climate as they act as filters of carbon dioxide. Forests are known as habitats and shelters of millions of species. However, the trees on our planet are being depleted at very high rates. The deforestation that has taken place due to human activity is as big as 50% of the whole planet. The main causes of deforestation is Ranching, Plantations, Logging, Mining, Road Building, Shifting Cultivations and for other commercial purposes. The destruction of the forests is occurring due to various reasons, one of the main reasons being the short-term economic benefits. Urban Construction is the main reason why large area of land is cleared. This involves cutting down of trees for lumber that is used or buildi ng materials, furniture and paper products which have a major impact on forest life. Forests are cleared to accommodate expanding urban areas. Road building is also included in these developments and one successful link is the Trans-Amazonian highway. This results in loss of forest area and massive deforestation. There are also local causes such as the Agricultural reasons. Forests are also cut down to clear land for growing crops, build farms, ranches and other food growing lands. The process of plantation is one of the causes which increased deforestation rates. It clears a patch of land to grow crops by slash and burn. The patch is then deserted until the soil regains its fertility. While plantation clears land by burning it, Shifting Cultivation still is as bad as Plantations as a large agricultural area is usually used for growing one crop such as bananas, coffee, cocoa and rubber. This process is usually carried out by international and therefore deforestation again is for short-term economic benefits. A main harvest in Brazil is Soybeans. This type of growing brings huge amount of profit towards the government. Even though most of the deforestation is caused for economic reasons there are some local/personal reasons such as Ranching. Large-scale cattle rearing-: because of this farms are huge to ensure there is enough grass to feed cattle. This gives land for cows to graze on. This is a main business as main retailers like McDonalds buy huge amounts of beef from places like the rainforest as they get it for cheap prices. Commercial Purpose for many large companies is another causation of deforestation. Companies clear forest for oil and mining exploitation to make highways and roads. Natural reasons are a big problem as well due to acid rain and wildfires which spread swiftly across large areas of forest land. Forest fires can occur naturally or in most cases are deliberate attempts by man to clear huge deforestation. Most of the time, these forest may recover, but usually the cleared land is used for construction and agricultural purposes. This leads to loss of forest and loss of habitat for the local wildlife. Mining – removal of minerals from the ground e.g. copper, gold and iron ore form large mines require clearing of large forest land. Mining is a legal process but there is illegal logging to use timber for commercial reasons e.g. mahogany has a big market for furniture in MEDCs. In Brazil 80-90% of logging is illegal. The WWF, the worldwide fund (non-government organisation) said that 28% of the EU’s timber imports could be illegal. Therefore there are economic are local reason which causes deforestation.

Democracy And Individualism A Nation Of A Homogenous...

Democracy and Individualism In the 1800’s, Thomas Jefferson, Andrew Jackson, and many others had visions for America that involved a nation of a homogenous type of society. It was believed in order to create a better nation that people other than the European Americans needed to be eradicated. In these beliefs, these men affected the America nation through their trials and tribulations, which help guide society into what it is today. Thomas Jefferson was a man who viewed white as beautiful. In which his views of black and Native Americans played a vital role in the development of the frontier. He viewed America as a Republic society with only room for white people. So, he envisioned creating a pure group of white people that could attune†¦show more content†¦Jefferson believed then once paid in full he would release his slaves upon the payment of his debts. Although his beliefs, he died before paying his debt off still owning slaves. 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