Simultaneous determination of catecholamines, uric acid and ascorbic acid at

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尿酸在聚亚甲基蓝修饰金电极上的电化学及电化学动力学性质

尿酸在聚亚甲基蓝修饰金电极上的电化学及电化学动力学性质
图 2 1. 0 ×1023 mol·L21UA在 Au ( b)和 PMB /Au ( c)上的循环伏安曲线. Fig. 2 The CV curves of 1. 0 ×1023 mol·L21 UA at ( b) Au, ( c) PMB /Au electrode and PMB /Au ( a) in
(1. 北方民族大学 ,预科教育学院 ,宁夏 银川 750021; 2. 宁夏大学能源化工重点实验室化学化工学院 ,宁夏 银川 750021)
关键词 :尿酸 ;聚亚甲基蓝 ;修饰电极 ;电化学性质 中图分类号 : O657 文献标识码 : A
尿酸 (U ric acid, UA )是人体内嘌呤核苷酸分 解代谢过程中的最终产物 。体液中尿酸的含量变 化可以充分反映出人体新陈代谢 、免疫等机能状 况 ,同时 也 可 间 接 反 映 出 与 嘌 呤 代 谢 的 有 关 疾 病 [ 1 ] 。有关 UA 在修饰电极上的电化学分析方法 研究已有不少相关文献报道 ,如多壁炭纳米管修 饰电极 [ 2 ] ,生物胆碱修饰电极 [ 3 ] ,自组装修饰金电 极 [ 4 ]等 [ 527 ] 。
在 20. 10 ~ 1. 0 V 电位窗口及 0. 10 mol·L21 PB S (pH 6. 8 ) 水溶液中研究了 1. 0 ×1023 mol·L21 UA 在裸 Au和 PMB /Au上的循环伏安行为 ,如图 2所示 。UA 在 Au电极上 (图 2b曲线 ) Epa为 770 mV ,而在 PMB /Au 上 (图 2c 曲线 ) Epa为 700mV。 与裸 Au相比 , UA 在 PMB /Au上 Epa负移 70 mV , Ipa明显增大 。表明 PMB /Au对 UA 的电化学氧化 产生了催化作用 。催化的可能原因是 : UA ( pKa = 5. 80)在 PBS ( pH6. 8 )水溶液中以阴离子形式存 在 [ 13 ] ,而 MB 中 2N ( CH3 ) 2与 H +结合成阳离子 ,同 时 MB 发生电化学氧化成为氧化态 ,使得 MB 修饰 电极表面带有高密度的正电荷 ,两者存在强烈的 静电相互作用 , UA 与氧化态 MB 发生化学反应被 催化氧化 , MB 被还原 ,从而导致 UA 的氧化峰电 位负移 ,峰电流 Ipa增加 。

Determination of catecholamines in pheochromocytoma cell

Determination of catecholamines in pheochromocytoma cell

Journal of Chromatography A,870(2000)405–411/locate/chromaDetermination of catecholamines in pheochromocytoma cell (PC-12)culture medium by microdialysis–microbore liquidchromatographya,e ,a abc *Fu-Chou Cheng,Jon-Son Kuo ,Hsueh-Meei Huang ,Dar-Yu Yang ,Tsu-Fang Wu ,dTung-Hu Tsai aDepartment of Medical Research ,Taichung Veterans General Hospital ,Taichung 407,Taiwan bDepartment of Emergency ,Taichung Veterans General Hospital ,Taichung 407,Taiwan cInstitute of Biochemistry ,Chung Shan Medical &Dental College ,Taichung 402,Taiwan dDepartment of Pharmacology ,National Institute of Chinese Medicine ,Taipei 112,Taiwan eDepartment of Chemistry ,National Chung -Hsing University ,Taichung 402,TaiwanAbstractAn in vitro microdialysis system was constructed for the measurement of catecholamines in pheochromocytoma cell culture medium.The novel microdialysis device is composed of a petri dish,a dialysis membrane and two transmission tubes.The dialysis membrane is located in the space of a petri dish such that it is immersed in the culture medium.Catecholamines contained in the culture medium diffused into a designed dialysis membrane with sufficient recovery (about 60%).Dialysates were collected by a sampling loop and introduced by an on-line injector to a microbore liquid chromatographic system for analysis of catecholamines.This assay yielded a detection limit of 0.2–0.5pg/injection with acceptable intra-and inter-assay reproducibilities in 5m l of dialysates.To evaluate the on-line microdialysis system,PC-12cells were cultured in a petri dish within an incubator.The baseline concentration of dopamine in PC-12cell culture medium was about 0.29ng/ml which was elevated to 2.43ng/ml after treatment with 0.5m M potassium cyanide.In conclusion,the present microassay provides for the sensitive,direct measurement of catecholamines in culture medium while minimizing pretreatment procedures for sample preparation.©2000Elsevier Science B.V .All rights reserved.Keywords :Pheochromocytoma cells;Catecholamine1.Introductionfunctions in the peripheral and central nervous systems,and have been implicated in the neuro-Microdialysis is one of the most widely used chemistry and physiology of mental diseases and techniques for in vivo or in vitro sampling of the neurological disorders [2,3].Measurements of cat-chemical substances in extracellular fluids of animal echolamines utilizing high-performance liquid chro-tissues,or cultured cells [1].Catecholamines and matography (LC)and electrochemical detection their related compounds play a number of important(ED)[4]are useful in investigating the etiology of neurological disorders in animal models or cell cultures [5–7].Recently,microbore LC–ED detec-*Corresponding author.Tel.:1886-4-359-2525;fax:1886-4-tion has led to sub-femtomolar detection for cat-359-2705.E -mail address :c1035@.tw (F.-C.Cheng)echolamines [8–10].Microdialysis and microbore0021-9673/00/$–see front matter ©2000Elsevier Science B.V .All rights reserved.PII:S0021-9673(99)00910-3406F.-C.Cheng et al./J.Chromatogr.A870(2000)405–411LC–ED technique are complementary tools that are describe an on-line in vitro microdialysis-microboreroutinely used in this laboratory to study extracellu-LC–ED technique for the measurement of catechol-lar catecholamines or their metabolites in rat brain amines in PC-12cell culture medium.[8–10].In vitro microdialysis studies were alsocarried out in biologicalfluids[11]and tissueschambers[12,13].Dynamic secretion of steroids and 2.Experimentalpeptides in corpus luteum were carried out in aprolonged time by Maas et al.[12].Similarly,The microdialysis microbore LC–ED was com-oxytocin stimulates progesterone release from mi-prised of a micropump(CMA-100,CMA,Stock-crodialysated bovine corpus luteum was demonstra-holm,Sweden),an on-line injector(CMA-160),a ted in vitro by Miyamato and Chams[13].Microtech LC-pump(Micro-tech Scientific,Sunny-Pheochromocytoma cells(PC-12)resemble adre-vale,CA),a BAS-4C electrochemical detector nal chromaffin cells which share many physiological(Bioanalytical Systems,Inc.,West Lafeyette,IN),a and pharmacological properties of neurons[14–16].Beckman I/O406interface(AI-406),Beckman PC-12cells synthesize,store,and secrete dopamine System Gold Data Analysis Software(Beckman (DA)and norepinephrine(NE)[15].On stimulation,Instrument Inc.,Taiwan Branch),and a microbore PC-12cells release catecholamines by exocytosis reversed-phase columnfilled with Inertsil ODS-2 [16].Many studies have been carried out on PC-12(GSK-C,5m m ODS, 1.03150mm I.D.,GL18cells via catecholamine determination to investigate Sciences Inc.,Tokyo,Japan).The potential for the how particular drugs affect the release or uptake of glassy carbon working electrode was set at10.75V, dopamine by PC-12cells[15–17].In general,PC-12with respect to a Ag/AgCl reference electrode[18]. cells have been plated in culture dishes and incu-Chromatograms were recorded on the Beckman I/O bated in an incubator.At different times after406interface,and analyzed via the Beckman System incubation or certain treatments,the supernatant of Gold Data Analysis Software.To increase the de-cells are removed and analyzed via conventional tection sensitivity of the microbore LC system,a pretreatment prior to LC–ED analysis.There is no very thin spacer(16m m)was used instead of a difficulty in the measurement of intracellular cat-conventional one(51m m)to create a sub-microliter echolamines in PC-12cells because of their rela-thin-layer electrochemical cell.Very slowflow-rates tively high concentrations(20–200ng/ml).How-were used to minimize pulsefluctuations and noise. ever,the measurement of extracellular catechola-NE,EPI,DA,DOPAC,ethylenediaminetetraacetic mines in culture medium using conventional LC–ED acid(EDTA),1-octanesulfonate(SOS),NaOH,and has been difficult and challenging.First,the extreme-N-[2-hydroxyethyl]piperazine-N9-[2-ethanosulfonic ly low concentration of catecholamines in medium acid]sodium salt(HEPES)were purchased from requires an analytical detection limit in low pico-Sigma(St.Louis,MO,USA).HPLC grade acetoni-grams for successful measurement.Second,it is trile(CH CN)and tetrahydrofuran(THF)were3necessary to centrifuge the cells andfiltrate cell obtained from E.MERCK(MERCK-Schuchardt, debris to collect the culture medium,which may Darmstadt,Germany).Monochloroacetic acidcause contamination of PC-12cell culture system.(CH ClCOOH)was purchased from BDH Labora-2Third,the detected catecholamine concentrations in tory Supplies(BDH Laboratory Supplies,Poole, the PC-12cell culture medium are often low which UK).Unless otherwise stated,all reagents were of may result in either difficulty in analysis or unreli-analytical quality.able data from conventional LC–ED.Fourth,the PC-12cells were grown in NUNC T75flasks medium samples require time-consuming pretreat-(Naperville,IL)in Dulbecco’s Modified Eagle’s ments or complicated extraction prior to analysis by Medium(DMEM,Gibco,Gaithersburg,MD)sup-conventional LC–ED assays,which may result in plemented with5%horse serum and10%fetalsample losses and increases in the amount of time bovine serum(FBS),and maintained in a10%CO2 necessary to complete experiments.Based on Maas humidified incubator at378C as previously described et al.and Miyamoto and Schams studies[12,13],we[19].PC-12cells were cultured on35mm petri dishF.-C.Cheng et al./J.Chromatogr.A870(2000)405–411407 with DMEM.The working buffer was prepared by transmission tubes jutted out through the holes in the dissolving0.17g HEPES in25ml liquid medium of cover.The bottom ends of the transmission tubes DMEM Base,which contained L-glutamine,phenol were located in the receiving space of the main body, red,and sodium pyruvate.Then,the pH of the buffer and curved such that the longitudinal central line of was adjusted to7.4.the bottom ends and the longitudinal central line of The standard stock solutions of NE,EPI,DOPAC,the transmission tubes formed a predetermined angle. and DA were prepared at a concentration of2m g/ml The outer wall surface of the transmission tubes and in0.1M perchloric acid and stored at2708C in the the inner wall surface of the holes of the cover were dark.For the daily preparation of a standard mixture,secured by sealing material.The dialysis tube(D) a portion of these stock solutions was thawed at48C was made of a dialysis membrane(Spectrum,20mm and diluted to the appropriate concentration of20length,150m m outer diameter with a cut-off at27ng/ml with a solution containing10M ascorbic nominal molecular weight of13000,Laguna Hills, acid in0.1M HCl.CA),and was immersed in the PC-12cell culture The buffer consisted of9.60g monochloroacetic medium(C)as shown in Fig.1.acid,0.16g sodium1-octane sulfonate,and10mg The sampling device was perfused with the work-EDTA,adjusted to pH3.0with1M sodium hy-ing buffer at2m l/min by a micropump(CMA-100). droxide.Thefinal volume of the mixture was Microdialysates were introduced by an on-line injec-adjusted to1l with doubled distilled water.The tor(CMA-160)and analyzed by a microbore LC–mobile phase was prepared by mixing50ml acetoni-ED at30min intervals.Following a3h baseline trile and950ml phosphate buffer.The solution was collection,KCN was introduced to give afinal filtered through a nylonfilter under reduced pressure concentration of0.5m M KCN in the culture and degassed with helium for15min.Theflow-rate medium.PC-12cells under KCN-induced hypoxia was80m l/min,and the column pressure was were incubated for an additional5h.The equipped maintained at ca.12.4MPa.on-line injector(CMA-160)was used to collect As illustrated in Fig.1,a sampling device is microdialysates.Five m l of aliquots of mi-composed of a petri dish(B and E),two transmission crodialysates were automatically assayed for cat-tubes(A),and a dialysis membrane(D).The petri echolamines by a microbore LC–ED while the petri dish had a receiving space with an open top.The dish was kept in an incubator.cover contained with two holes separated by a Prior to the experiments,in vitro recovery was predetermined distance.This microdialysis system is performed using a standard mixture containing cat-similar to those reported by Mass et al.[12]and echolamines,to determine the recoveries of all Miyamato and Chams[13].The top ends of the two analytes and the dead volume(ca.36m l)of themicrodialysis system.Experimental data were re-corded and analyzed via the Beckman System GoldData Analysis Software.3.Results and discussionFig.2A shows a typical chromatogram of astandard mixture(ca.0.02ng/ml each)containingNE(3.6min),EPI(4.8min),DOPAC(6.9min),andDA(9.4min).Analysis was completed within10min.Fig.2B and C show typical chromatograms ofmicrodialysates obtained from PC-12cell culturemedium.All components under study were well Fig.1.A schematic diagram of a novel dialysis petri dish.(A):resolved.Retention times of NE,DOPAC,and DA in Transmission tubes;(B):Petri dish cover;(C):Culture medium;(D):Dialysis membrane(20mm in length);(E):Petri dish body.Fig.2A,B,and C were identical.In the preliminary408F.-C.Cheng et al./J.Chromatogr.A870(2000)405–411Fig.2.Typical chromatograms obtained from(A)a standard mixture containing(1)NE,(2)EPI,(3)DOPAC,and(4)DA;(B)a microdialysis of baseline;and(C)a microdialysate after KCN-induced hypoxia.F.-C.Cheng et al./J.Chromatogr.A870(2000)405–411409Table2experiments,EPI was always undetectable in cultureAnalytical precision on the stabilities of intra-assay(n512,at1h medium.which was in agreement with other inves-intervals)and inter-assay(n56,in six consecutive working days) tigators[20].The baseline concentrations of NE,of standard mixtures and PC-12cells dialysates in the microbore DOPAC,and DA in PC-12cell culture medium were LC–ED system0.77,0.55and0.29ng/ml,respectively.SeveralCoefficient of variation(%) unknown peaks appeared within30min.In order toNE EPI DOPAC DA prevent carry-over peaks from previous runs,acomplete run was set at30min.Intra-assayStandard mixtureIn general,the amounts of each injected analytein0.1M HClwere linearly related to chromatographic areas ob-(ca.1pg each) 3.9 2.4 6.2 2.42tained from standard mixtures(R$0.999)over a(ca.50pg each) 2.3 3.5 4.2 2.1large range of concentrations(1–2000pg,Table1)PC-12cellsin microbore LC–ED.However,calibration curvespooled dialysates 4.8N.D. 5.2 3.3 were constructed with three standard mixtures(con-taining ca.1,10,and100pg of catecholamines,Inter-assayStandard mixturen53)prior to LC–ED analyses on the day ofin0.1M HClexperiments.Concentrations of NE,DOPAC,and(ca.50pg each) 4.3 5.2 5.3 4.0 DA in dialysates were determined by these cali-bration curves.The precision of the assays was tested using a the relative recovery and is usually expressed as astandard mixture and pooled dialysates of PC-12cell percent value.For in vitro microdialysis recovery,culture medium(Table2).The intra-assay var-the dialysis device was calibrated in a standardiabilities were assessed with12replicates at1h solution containing100ng/ml of each analyte.Theintervals and expressed as coefficients of variation working buffer solution was perfused atflow-rates(C.V.,%).The intra-(n512)and inter-assay(n56)ranging from0.3to 5.0m l/min.The in vitrovariabilities were assessed and the C.V.values of all recovery(R%)of each analyte was calculatedin v itroanalytes in dialysates were less than7%.In general,from the concentration of each analyte(C)inoutthe C.V.s for DA and NE were lower than the C.V.s dialysates divided by the concentration of the analytefor EPI and DOPAC in the chromatographic mea-in the petri dish(C).The higher the perfusioninsurements.The detection limits(signal-to-noise ratioflow-rate,the lower the recovery as shown in Table53)of all analytes in the present assay were 3.In general,experiments were carried out at1.0–between0.2and0.5pg per injection(or0.04–0.1 3.0m l/min to collect sufficient amount of samples ng/ml).and to overcome the dead volume of the dialysis The concentration of an analyte in the dialysate device.The perfusionflow-rate wasfixed at 2.0 relates to the concentration of that analyte in the m l/min in the present study(recovery values be-PC-12cell culture medium.This relation is called tween56and66%).In vitro recovery values of allTable1Table3Correlation of anodic current with the amount of biogenic amines,In vitro recovery values(%)of catecholamines at varied perfusion and their metabolites in standard mixtures(ranging from1pg toflow-rates for the novel dialysis device2000pg)measured by the microbore LC–ED systemFlow rate(m l/min)NE EPI DOPAC DAa2Standard curve equation R0.393998797 NE Y54020X13 1.0000.589928190 EPI Y53865X1140.9991828273791.572726371 DOPAC Y56360X25 1.000265665664 DA Y55880X118 1.000350514250529312731a Y5peak area measured;X5amount of analytes in pg.410F.-C.Cheng et al./J.Chromatogr.A870(2000)405–411analytes at 2.0m l/min were also recorded and late.The entire time profiles of catecholamines validated on each dialysis device prior to experi-obtained from PC-12cell culture medium before and ments.after KCN-induced hypoxia are shown in Table4.It Extracellular catecholamine concentrations in is evident that these analytes varied very soon after dialysates of PC-12cells did not change much within administration of KCN.In general,increased release an8h period as shown in Table4.However,NE of catecholamines was demonstrated during KCN-concentrations(0.77ng/ml at baseline)dramatically induced hypoxia.These data are in agreement with increased to15.8ng/ml within5h after0.5m M those of other investigators[22,23].However,the KCN treatment,as shown in Table 4.DOPAC detailed mechanism of the release of catecholamines concentrations(0.55ng/ml at baseline)slowly in-during KCN-induced hypoxia requires further in-creased to about3fold of baseline(1.84ng/ml)at5vestigation.h after0.5m M KCN treatment.DA concentrations The present method requires no pretreatment of demonstrated a transient elevation(18fold,from samples,whereas conventional pretreatment proce-0.29to 2.43ng/ml)at the beginning of KCN dures require more than4hours to prepare8–10 treatment and drastically decreased to relatively samples[24–26].The cumbersomeness of pretreat-lower levels(about two folds of baseline)within3h ment procedures of small volumes of culture medium after0.5m M KCN treatment.The mechanism by is still a problem for culture systems.Another which KCN increased catecholamine levels in the advantage of this method is its low detection limits extracellular space probably reflects both an in-(0.2–0.5pg/per injection,typically).This on-line creased release of catecholamines into the medium as method can increase the experimental speed,provide well as a decreased removal of these substances from high sensitivity,minimize required sample volume, the medium.Removal of substances from the enhance detection limits,and decrease degradation of medium is largely due to an uptake mechanism the analyzed compounds.which is an adenosine triphosphate(ATP)-dependent In vitro microdialysis system described by Maas et process.KCN-induced hypoxia is known to cause al.[12]and Miyamoto and Schams[13]was modi-ATP depletion[21].Therefore,the uptake mecha-fied.An autosampler and an incubator were used in nism is blocked and catecholamine levels accumu-this study.In conclusion,the dialysis device is Table4Concentrations of NE,DOPAC,and DA in PC-12cell culture medium dialysates obtained from petri dishes incubated under control or KCN treatmentTime(h)NE DOPAC DAControl KCN Control KCN Control KCN 0.50.16 1.030.250.240.100.18 10.48 1.770.230.310.140.25 1.50.58 1.810.210.400.070.18 20.73 1.980.220.580.090.13 2.50.91 1.740.420.640.050.19 a30.570.770.500.550.310.29 3.50.60 3.160.450.690.540.53 40.53 4.210.47 1.020.07 2.43 4.50.63 5.480.60 1.240.07 1.51 50.508.340.61 1.200.190.99 5.50.499.620.550.920.080.61 60.419.940.42 1.080.020.57 6.50.5712.510.78 1.080.230.65 70.5112.770.66 1.520.380.52 7.50.4915.060.78 1.840.220.7880.7315.800.71 1.840.140.48a KCN was given at3h.F.-C.Cheng et al./J.Chromatogr.A870(2000)405–411411[3]D.M.A.Mann,P.O.Yates,B.Marcyniuk,Clin.Neuropathol. capable of taking samples for examining the ex-3(1984)199.tracellular catecholamines with minimal disruption of[4]E.Kempf,P.Mandal,Anal.Biochem.112(1981)223. the normal growth of cells in PC-12cell culture.The[5]C.Y.Chai,A.M.Y.Lin,C.K.Su,S.R.Hu,L.S.Kao,J.S.Kuo, device also avoids contamination of cell culture and D.S.Goldstein,J.Auton.Nerv.Syst.33(1991)35. minimizes the disturbance on the closed system for a[6]C.A.Altar,M.R.Marien,J.F Marshall,J.Neurochem.48(1987)390.prolonged period of time.Microdialysis samples are[7]H.Nissbrandt,A.Carlsson,J.Neurochem.49(1987)59. free from impurities and macromolecules and can be[8]F.C.Cheng,L.L.Yang,F.M.Chang,L.G.Chia,J.S.Kuo,J. directly analyzed via LC.Microbore LC–ED has theChromatogr.B582(1992)19.advantages of signal enhancement and noise reduc-[9]F.C.Cheng,J.S.Kuo,J.Chromatogr.B665(1995)1. tion.As a result,low detection limits and short[10]F.C.Cheng,Y.Shih,Y.J.Liang,L.L.Yang,C.S.Yang,J.Chromatogr.B682(1996)195.analysis times can be obtained.The novel dialysis[11]F.C.Cheng,L.L.Yang,F.M.Chang,L.G.Chia,J.S.Kuo,J. device described in the present study is relativelyChromatogr.582(1992)19.simple in construction and is compatible with an[12]S.Maas,H.Jarry,A.Teichmann,W.Rath,W.Kuhn,W. on-line injection analyzer.The present study is Wuttke,J.Clin.Endocrinol.Metab.74(1992)306. relatively efficient,cost-effective,and less vulnerable[13]A.Miyamoto,D.Schams,Biol.Reprod.44(1991)1163.[14]Y.Shoji-Kasai,A.Yoshida,K.Sato,T.Hoshino,A.Ogura, to human error,as compared with conventionalS.Kondo,Y.Fujimoto,R.Kuwahara,R.Kato,M.Takahashi, studies in which a number of petri dishes are used.Science256(1992)1820.Indeed,the present study minimizes pretreatment[15]L.A.Greene,A.S.Tischler,A73 procedures for sample preparation,decreases pos-(1976)2424.sible contamination from sampling of culture[16]M.Schultzberg,C.Andersson,A.Under,M.Troye-Blom-berg,S.B.Svenson,T.Bartfai,Neuroscience30(1989)805. medium,and enhances the detection sensitivity of[17]H.M.Huang,L.S.Kao,J.Neurochem.66(1996)124. catecholamines in PC-12cell culture medium.Fur-[18]F.C.Cheng,J.S.Kuo,Y.Shih,i,D.R.Ni,L.G.Chia, thermore,this novel microdialysis device can also beJ.Chromatogr.B615(1993)225.applied to the measurement of chemical substances[19]L.A.Greene,A.S.Tischler,Adv.Cell.Neurobiol.3(1982) in other culture systems.373.[20]F.Bussolino,F.Tessari,F.Turrini,P.Braquet,G.Camussi,M.Prosdocimi,A.Bosia,Am.J.Physiol.255(24)(1988)C559.Acknowledgements[21]Y.Cheng,P.Wixom,M.R.James-Kracke, A.Y.Sun,J.Neurochem.63(1994)895.This study was supported in part by grants from[22]A.G.Kanthasamy,E.U.Madhu,R.W.Peoples,J.L.Borowitz,G.E.Isom,Toxicol.Appl.Pharmacol.110(1991)275. Taichung Veterans General Hospital(TCVGH-[23]G.K.Kumar,J.L.Overholt,G.R.Bright,K.Y.Hui,H.W.Lu, 897304C)and the National Science Council(NSC-M.Gratzl,N.R.Prabhakar,Am.J.Physiol.274(1998) 88-2113M-075A-002)of the Republic of China.C1592.[24]J.Odink,H.Sandman,W.H.P.Schreurs,J.Chromatogr.377(1986)145.[25]M.Picard, D.Olichon,J.Gombert,J.Chromatogr.341 References(1985)297.[26]G.Eisenhofer, D.S.Goldstein,R.Stull,H.R.Keiser,T.[1]T.E.Robinson,J.B.Justice Jr.(Eds.),Microdialysis in the Sunderland,D.L.Murphy,I.J.Kopin,Clin.Chem.32(1986)Neurosciences,Elsevier Science,Netherlands,1991,p.1.2030.[2]H.Yao,K.Fukiyama,Y.Takada,M.Fujishima,T.Omae,Jpn.Heart J.37(1985)593.。

电活化玻碳电极循环伏安法测定对苯二酚的研究

电活化玻碳电极循环伏安法测定对苯二酚的研究

电活化玻碳电极循环伏安法测定对苯二酚的研究张东霞;薛蛟玉【摘要】研究简化电极处理过程测定环境水样中对苯二酚含量的效果.以电活化的玻碳电极为工作电极,采用循环伏安法测定环境水样中对苯二酚的含量.结果表明,电活化的玻碳电极对对苯二酚的氧化还原反应有明显的电催化作用,对苯二酚的氧化还原峰电流与其浓度在1×10-6~l × 10-4 mol/L范围内呈现良好的线性关系.电活化的玻碳电极具有良好的重现性,用该方法测定了环境水样中对苯二酚的含量,回收率为93.8%~103.6%,结果令人满意.从而建立一种简便、快速、准确的测定环境中对苯二酚含量的方法.【期刊名称】《应用化工》【年(卷),期】2016(045)006【总页数】4页(P1187-1190)【关键词】对苯二酚;循环伏安法;玻碳电极;测定【作者】张东霞;薛蛟玉【作者单位】西京学院应用理学系,陕西西安710123;西京学院应用理学系,陕西西安710123【正文语种】中文【中图分类】TQ150.1;TQ160.9;O657.1对苯二酚在化工领域用途广泛,是制造有机染料及医药的重要原料,常用作洗发液中氧化染料,也用作照相的显影剂、橡胶的抗氧化剂及洗涤剂的稳定剂。

但对苯二酚具有毒性,残余废弃物进入环境,会对环境造成污染,并且难以降解[1]。

通过吸入,经皮吸收等方式进入人体,会损害人体健康,重度中毒可导致死亡[2]。

因此,环境中对苯二酚的测定一直是环境监测工作人员研究的热点。

目前测定对苯二酚的方法有高压液相色谱法[3]、电化学分析法[4-6]、光度法[7]、化学发光法[8]等。

其中电化学方法由于其操作简便、灵敏度高、反应快速等优点,成为环境检测中最常用的分析技术。

玻碳电极是电化学分析中使用最广泛的碳材料基础电极,具有电势适用范围宽、硬度高和热膨胀系数小等特点。

但玻碳电极表面性质不稳定,每次使用前经过打磨、清洗,仍不能满足对灵敏度要求较高的分析测试。

11、HPLC同时测定麦冬药材中3种黄酮类成分的含量_贾诚

11、HPLC同时测定麦冬药材中3种黄酮类成分的含量_贾诚

基金项目:“国家重大新药创制”科技重大专项(2010ZX09502-004);科技创新专项资金(08FDZDSH01404)作者简介:贾诚,男,硕士研究生研究方向:中药新药研发*通讯作者:叶正良,男,研究员研究方向:中药新药研发Tel :(022)HPLC 同时测定麦冬药材中3种黄酮类成分的含量贾诚1,2,叶正良2*,姜秀晶1,周大铮2,李德坤2(1.天津中医药大学中药学院,天津300193;2.天津天士力之骄药业有限公司,天津300402)摘要:目的测定麦冬药材中甲基麦冬黄烷酮A 、甲基麦冬黄烷酮B 和6-醛基异麦冬黄烷酮A 的含量,为麦冬药材的质量控制提供科学依据。

方法采用Waters Symmetry C 18柱(4.6mm ˑ250mm ,5μm ),乙腈-0.05%磷酸梯度洗脱,流速为1.0mL ·min -1,检测波长296nm ,柱温30ħ。

结果甲基麦冬黄烷酮A 、甲基麦冬黄烷酮B 和6-醛基异麦冬黄烷酮A 分别在9.6896.8、4.96 49.6、4.18 41.8μg ·mL -1内具有良好的线性关系,平均回收率(n =6)分别为100.1%(RSD 1.03%),99.5%(RSD 1.35%)和100.2%(RSD 1.16%)。

结论该方法快速、准确,可用于麦冬药材中甲基麦冬黄烷酮A 、甲基麦冬黄烷酮B和6-醛基异麦冬黄烷酮A 的含量测定。

关键词:麦冬;甲基麦冬黄烷酮A ;甲基麦冬黄烷酮B ;6-醛基异麦冬黄烷酮A ;HPLC 中图分类号:R283文献标志码:A文章编号:1001-2494(2011)15-1209-03Simultaneous Determination of Contents of Three Flavonoid Ingredients in Radix Ophiopogonis by HPLCJIA Cheng 1,2,YE Zheng-liang 2*,JIANG Xiu-jing 1,ZHOU Da-zheng 2,LI De-kun 2(1.Tianjin University of TraditionalChinese Medicine ,Tianjin 300193,China ;2.Tianjin Tasly Pride Pharmaceutical Company Limited ,Tianjin 300402,China )ABSTRACT :OBJECTIVETo determine the contents of methylophiopogonanone A ,methylophiopogonanone B and 6-aldehydo-isoophiopogonone A in Radix Ophiopogonis.METHODSWaters Symmetry C 18column (4.6mm ˑ250mm ,5μm )was used withphosphoric acid (0.05%,v /v )and acetonitrile as the mobile phase.Stepwise gradient elution was adopted.The flow rate was 1.0mL ·min -1,the detection wavelength was 296nm ,and the column temperature was maintained at 30ħ.RESULTSThe calibrationcurves showed good linearity within the range of 9.68-96.8,4.96-49.6and 4.18-41.8μg ·mL -1for methylophiopogonanone A ,methylophiopogonanone B and 6-aldehydo-isoophiopogonone A ,respectively.The mean recoveries (n =6)were 100.1%(RSD 1.03%),99.5%(RSD 1.35%)and 100.2%(RSD 1.16%),respectively.C ONCLUSION This method is simple and accu-rate.And it can be used for the determination of methylophiopogonanone A ,methylophiopogonanone B and 6-aldehydo-isoophio-pogonone A in Radix Ophiopogonis .KEY WORDS :Radix ophiopogonis ;methylophiopogonanone A ;methylophiopogonanone B ;6-aldehydo-isoophiopogonone A ;HPLC麦冬来源于百合科植物麦冬[Ophiopogon ja-ponicus (Thunb.)Ker-Gawl.]的干燥块根。

JEAC Sensitive simultaneous determination of diethylstilbestrol and bisphenol

JEAC Sensitive simultaneous determination of diethylstilbestrol and bisphenol

Sensitive simultaneous determination of diethylstilbestrol and bisphenol A based on Bi 2WO 6nanoplates modified carbon pasteelectrodeLei Peng a ,Sheying Dong a ,b ,⇑,Huidong Xie a ,Guangzhe Gu a ,Zhixian He a ,Jinsuo Lu b ,Tinglin Huang b ,⇑a College of Sciences,Xi’an University of Architecture and Technology,Xi’an 710055,ChinabSchool of Environmental and Municipal Engineering,Xi’an University of Architecture and Technology,Xi’an 710055,Chinaa r t i c l e i n f o Article history:Received 22December 2013Received in revised form 14April 2014Accepted 3May 2014Available online 13May 2014Keywords:Bi 2WO 6nanoplates Modified electrodeSimultaneous determination Diethylstilbestrol Bisphenol Aa b s t r a c tBi 2WO 6nanoplates were hydrothermally prepared and characterized by scanning electron microscopy (SEM)and X-ray diffraction (XRD).The synthesized Bi 2WO 6nanoplates were then used to fabricate mod-ified carbon paste electrode (Bi 2WO 6–CPE)by a simple rubbing method.The result of electrochemical impedance spectroscopy indicated electron transfer resistance of the Bi 2WO 6–CPE was reduced vastly compared with CPE.In the meantime,cyclic voltammetry experiment demonstrated the Bi 2WO 6nano-plates could accelerate the rate of electron transfer for the electrochemical reaction of diethylstilbestrol (DES)and bisphenol A (BPA)on the electrode.Moreover,the as-prepared electrode exhibited good selec-tivity toward simultaneous determination of DES and BPA with a rather low detection limit.By using dif-ferential pulse voltammetry (DPV)method,low detection limits of 15nM (S/N =3)and 20nM (S/N =3)for DES and BPA were obtained,with the linear calibration curves over the concentration range 50–2100nM and 70–1300nM,respectively.In addition,the proposedappliedfor thedetermination of analytes in spiked milk samples extracted from milk powder.Ó2014Elsevier rights reserved.1.IntroductionEnvironmental estrogens are endocrine-disrupting chemicals (EDCs)that have been defined as either natural or man-made agents that interfere with the natural action of endogenous hor-mones [1].Most of environmental estrogens can accumulate in the human body through food chain [2]and lead to harmful effects such as reproductive disorder,birth defects and cancer risk at a very low concentration [3].As a kind of typical environmental estrogen,diethylstilbestrol (DES)has been widely used in the treatment of estrogen-deficiency disorders and illegally used as a growth pro-moter in animal feed,which could result in negative health effects [4].At the same time,bisphenol A (BPA)is also widely used for the production of polycarbonates plastics and epoxy resins.Inevitably,it is released from many plastic packages,such as baby bottles,plas-tic food containers as well as inner surface coating of food and bev-erage cans,leading to food and environment pollution [5,6].In addition,the two compounds usually exist simultaneously in our living environment with a self-aggravating tendency from year to year.Thus,it is essential to develop a reliable,sensitive and high-selective method for the determination of DES and BPA in the food and Conventional analytical techniques for the determination of DES or BPA are mainly high performance liquid chromatography (HPLC)[7,8],liquid chromatography–mass spectrometry (LC–MS)[9,10],and gas chromatography–mass spectrometry (GC–MS)[11,12].Though these analytical techniques can achieve high sen-sitivity and good precision,they have to be operated trained technicians,and require time-consuming sample ment,making them unsuitable for on-site rapid comparison,electrochemical method is less expensive and has additional advantages of fast response speed,simple operation,timesaving,high sensitivity,excellent selectivity,and real-time detection in situ condition as an analytical technique [13]How-ever,DES or BPA exhibits slow electron transfer at bare electrodes,which leads to low sensitivity for their detection.Therefore,some functional materials have been synthesized to construct sensors for the sensitive detection of DES or BPA.For example,Liu et al.[14]constructed an electrochemical immunomodified electrode based on mesoporous nanocomposites and HRP-functionalized nanopar-ticles bioconjugates for sensitivity enhanced detection of DES.Zhang et al.[15]fabricated a sensor for fast selective detection of BPA using arginine functionalized nanocomposite graphene/10.1016/j.jelechem.2014.05.0081572-6657/Ó2014Elsevier B.V.All rights reserved.⇑Corresponding authors.Address:College of Sciences,Xi’an University of Architecture and Technology,Xi’an 710055,China.Tel.:+862982201203;fax:+862982205332(S.Dong).E-mail address:dongsyy@ (S.Dong).modified glassy carbon electrode.In addition,various DES or BPA sensors based on various materials including single-walled carbon nanotube/platinum nanoparticle composite film [16],graphene oxides [17],chitosan-Fe 3O 4[18],and cobalt phthalocyanize [19]were investigated.Under the optimized conditions,the detection limit was 15nM,3nM,8nM,10nM,respectively.Though low detection was achieved in those works,it is still a challenge to develop new and simple electrochemical sensor towards thedetectionof DES andBPA with highsensitivity andIn of sensors,CPE was usually preferred for its low cost and simple preparation procedure.Moreover,through the replacement of paraffin with different binders,the modifica-tion of the electrode surface,or the addition of new materials,the modified CPE exhibited an excellent electrochemical behavior [20].In the meantime,it is noteworthy that bismuth tungstate (Bi 2WO 6),a typical n-type direct band gap semiconductor with a band gap of 2.75eV,can act as a stable photocatalyst for the pho-tochemical decomposition of organic contaminants under visible light irradiation [21].Furthermore,its unique layered structure can enhance the photoactivity of Bi 2WO 6,in which the transfer of electrons to the surface was enhanced along the layered network [22].This promising Bi 2WO 6may have excellent application in the construction of electrochemical sensor due to its unique transfer ability of electrons.In this work,Bi 2WO 6nanoplates were synthesized by hydro-thermal process.A novel electrochemical sensor was constructed by coating CPE with Bi 2WO 6nanoplates,and the electrochemical behaviors of DES and BPA were studied by cyclic voltammetry (CV).The proposed sensor was successfully applied for the simul-taneous determination of DES and BPA in spiked milk samples with good recoveries.2.Experimental2.1.Chemicals and materialsDES was purchased from Wuhan Huayida Technology Limited Company,BPA was purchased from Chengdu Kelong Chemical Reagent Factory.Graphite powder,K 3Fe(CN)6,K 4Fe(CN)6,KCl,KH 2PO 4,K 2HPO 4Á3H 2O,Na 2WO 4Á2H 2O,Bi(NO 3)3Á5H 2O,NaOH were obtained from China National Medicine Corporation.All the chem-icals were of analytical reagent grade except graphite powder of spectrum pure and used without further purification.0.1M phosphate buffer solutions (PBS)with different pH values were prepared by mixing the stock standard solutions of K 2HPO 4and KH 2PO 4and adjusting the pH with 0.1M H 3PO 4and 0.1M NaOH.All solutions were made up with twice-distilled water.of Bi 2WO 6nanoplates and the Bi 2WO 6/CPE modified electrodesIn a typical procedure,Bi(NO 3)3Á5H 2O (2.4254g)was added into 30mL deionized water to form a suspension under magnetic stir-ring for 5min at room temperature.Then,30mL solution of dis-solved Na 2WO 4Á2H 2O (0.8246g)was slowly dropped into the suspension above,and adjusted pH to 1.0.The mixture solution was sealed in a 100mL Teflon-lined stainless steel autoclave and maintained at 180°C for 12h.The achieved light yellow product was filtrated,and washed several deionized water,and finally dried at a 100°C vacuum The CPE was prepared as follows:3.4g graphite powder and 0.6g liquid paraffin were mixed in an agate mortar and ground.The as-ground paste was packed into a cavity (3mm diameter)at the end of a Teflon tube.The electrical contact was providedby a copper wire to the paste in the inner hole of the tube.Prior to use,the of the as-prepared CPE was smoothed with a weighting The Bi 2WO 6/CPE was similar to the procedure described by the Ref.[23],which was as follows:1.5mg Bi 2WO 6nanoplates were placed on a piece of weight paper and the CPE was gently rubbed over the samples to make some of the material adhere to the elec-trode surface,and then smoothed again with a weighing paper.Before use,the Bi 2WO 6/CPE was treated in pH 6.0PBS by repetitive scanning in the potential range from À800to 800mV at the rate of 0.1V s À1until a stable blank background was obtained.2.3.The pretreatment of milk powder sample30mL of petroleum ether was added to the conical flask con-taining 5.00g of milk powder,and the mixture was placed under ultrasonic irradiation during 10min.After filtering and washing by petroleum ether,the filtrate was collected together to pass a 0.22l m polyvinylidene fluoride (PVDF)filter.The process was repeated twice in the same way,and the obtained solution was concentrated by rotary evaporation at 50°C to a microtube and then diluted to 2mL with methanol.Finally,the extract was obtained,and 0.5mL of the extract was added into 20mL pH 6.0PBS to perform the electrochemical experiment.2.4.Procedure and apparatusAll electrochemical measurement was carried out with a CHI660B electrochemical workstation (Shanghai Chenhua Co.)con-trolled by a microcomputer with CHI660software.A three elec-trode system was used,where an Ag/AgCl electrode (3.0M KCl,Shanghai Ruosull Tech.Co.)served as the reference electrode,a platinum wire electrode as the auxiliary electrode and a modified CPE as the working electrode.Cyclic voltammetric measurements were done in an undivided 30mL electrochemical Teflon cell at 25±0.5°C.DPV experiments were performed from 0.0V to 0.8V at pulse amplitude of 0.05V.All experimental solutions were deox-ygenated by purging them with highly pure nitrogen for 30min and maintained under nitrogen atmosphere during measurements.AC impedance experiments were carried out in 1.0mM K 3Fe(CN)6/K 4Fe(CN)6(1:1)containing 0.1M KCl,while the applied perturba-tion amplitude was 0.005V,the frequencies swept from 105to 10À2Hz,the number of points per frequency decade was 12and the initial potential was 0.20V vs.RE (Ag).The morphology of the prepared Bi 2WO 6nanoplates and the electrode surface were characterized by scanning electron micros-copy (SEM,JEOL JSM-5800,Japan)operated at an acceleration volt-age of 20.00kV.The powder XRD patterns were recorded with a Rigaku Dmax-rA X-ray diffractometer using Cu K a radiation.3.Results and discussion3.1.Characterization of Bi 2WO 6nanoplates and the electrodes The crystalline structure and morphologies of the sample were examined and the results were shown in Fig.1.As shown in Fig.1A,the diffraction data obtained match well with the orthorhombic symmetry Bi 2WO 6crystal phase (JCPDS card No.79-2381),and the expanded diffraction peaks revealed it was nanosized crystal-line phase.Furthermore,the SEM images in Fig.1B showed the morphologies of the sample.At a low-magnification view,many Bi 2WO 6clusters with average size of 4l m were flocked together loosely forming a lot of holes.At a high-magnification view (the inset of Fig.1B),these Bi 2WO 6clusters were piled up by numerous16L.Peng et al./Journal of Electroanalytical Chemistry 726(2014)15–20of nanosheets about 31nm in thickness,which was in accordance with the result of XRD.Besides,the surface morphologies of CPE (shown in Fig.S2(A)in Supplement Information )and Bi 2WO 6/CPE (Fig.S2(B)in Supple-ment Information )were also investigated by SEM.It can be seen that the surface of CPE was formed by irregularly shaped flakes.But for the Bi 2WO 6/CPE,a high-coverage Bi 2WO 6nanoplates monolayer is formed,and a random distribution and interstices among these nanoplates were observed in the SEM image,exhibit-ing a large surface area.3.2.Electrochemical performance of Bi 2WO 6/CPEimpedance spectroscopy (EIS)was often used interface changes of modified electrodes [24,25].semicircle part at higher frequencies corresponds transfer-limited process and its diameter is equal resistance (R ct ),which controls the electron redox probe at the electrode interface,while lower frequencies represents the diffusion-exhibited the representative impedance CPEand Bi 2WO 6/CPE in 1.0mM K 3Fe(CN)6/containing 0.1M KCl.In the high frequency sec-CPE was modified with Bi 2WO 6nanoplates,the R ct value decreased dramatically,suggesting a small interface R ct ,which was attributed to the electric conductivity of Bi 2WO 6nanoplates.These results also confirmed that the Bi 2WO 6nanoplates were successfully assembled onto the bare CPE surface.The electrochemical behaviors of different electrodes in the absence and presence of 1l M DES were investigated by CV in 0.10M pH 6.0PBS at a scan rate of 100mV s À1.As shown in the inset of Fig.2B,no redox peaks were observed on Bi 2WO 6/CPE without DES,indicating that Bi 2WO 6was non-electroactive in the selected potential window.When DES was added into 0.10M pH 6.0PBS,DES exhibited a poor redox current peak at the bare CPE within the potential windows from À0.2V to 0.8V,which indi-cated that DES underwent a quasi-reversible the CPE surface.However,on the Bi 2WO 6peaks were distinctly increased.This may Bi 2WO 6nanoplates with high surface area talysis activity.Furthermore,Bi 2WO 6nanoplates the electron transfer on the electrode surface trochemistry signal because of their good At the same time,CV responses of 1l M BPA CPE in 0.10M pH 6.0PBS were also Supplement Information ).The oxidation EIS of CPE and Bi 2WO 6/CPE;supporting solution:1mM K 3Fe(CN)6/K 4Fe(CN)6(1:1)containing 0.1M KCl.(B)CVs of 1l M DES on the (a)CPE and (b)Bi 26.0PBS at the scan rate of 0.1V s À1;inset:the CV of Bi 2WO 6/CPE in 0.1M pH 6.0PBS without DES.Fig.1.(A)XRD pattern and (B)SEM images of Bi 2WO 6nanoplates (inset:SEM images at high-magnification).the oxidation peak of DES and BPA appeared at about 550mV on Bi 2WO 6/CPE,respectively,along with a 170mV,which was broad enough for simultaneous cal determination.3.3.Effect of the scan rate and solution pHThe influence of the scan rate on the CV CPE was investigated (Fig.3A).Under the scan rate 0.7V s À1,the peak currents (i p )for DES were square root of scan rate (v 1/2)(inset,Fig.3A;linear regression equa-tions:I pa (l A)=1.581–8.085m 1/2(V s À1)(R =0.999,n =14),I pc (l A)=À3.309+64.71m 1/2(V s À1)(R =0.997,n =14)).Thus,the con-tribution of diffusion played a more important role in the electrode process of DES.Similar experiment demonstrated the electrode process of BPA was also controlled by diffusion (Fig.S3in Supple-ment Information ).The effect of pH on the current response of Bi 2WO 6/CPE to 1l M DES was investigated in the pH range from 3.0to 9.0.Fig.3B showed that the oxidation peak current gradually increased with the increase of the pH from 3.0to 6.0,and then decreased with the further increasing of pH,suggesting that protons had taken part in the electrode process [26].Considering the sensitivity of the determination of DES,the pH value of 6.0was chosen as the subsequent analytical experiments.The relationship between the redox peak potential (E p )and pH is also shown in inset of Fig.3B.It was found that the value of peak potential at Bi 2WO 6/CPE shifted to more negative potential with the increase of pH from 3.0to 9.0,and that it obeyed the following equations:E pa (V)=0.7282–0.05242pH (R =0.997,n =7);E pc (V)=0.3744–0.05094pH (R =0.978,n =7).A shift of typically 52mV and 51mV per pH unit demonstrated the electrooxidation of BPA at Bi 2WO 6/CPE is also a two electron and two-proton process,and can be illustrated by Scheme 1B.3.4.Calibration plot and limit of detectionAs a high sensitivity and a low detection limit electrochemical method,differential pulse voltammetric (DPV)was used for the determination of DES and BPA under the optimized conditions.The electrochemical responses of DES and BPA increase linearly with the increase of their concentration (Fig.4).The corresponding linear ranges for DES (Fig.4A)and BPA (Fig.4B)are 20–2300nM and 30–1300nM with detection limit of 9nM and 10nM at S/N =3,respectively.3.5.Simultaneous determination of DES and BPAFor simultaneous determination of DES and BPA at the Bi 2WO 6/CPE,DPV was carried out under the optimized conditions.In these measurements,only the concentration of the target analyte was (A)CVs of 1l M DES on the Bi 2WO 6/CPE in 0.1M pH 6.0PBS at different scan rates (0.08,0.10,0.15,0.20,0.25,0.30,0.35,0.40,0.45,0.50,0.55,0.60,0.65,0.70the plots of the redox peak currents vs.the square root of scan rate.(B)CVs of 1.0l M DES on the Bi 2WO 6/CPE under different pH (3.0,4.0,5.0,6.0,7.0,8.0,9.0)rate of 0.1V s À1.Inset:effects of pH on the redox potential of DES on the Bi 2WO 6/CPE.Scheme 1.Proposed reaction mechanism for the electrochemical oxidation of (A)DES and (B)BPA.18L.Peng et al./3.6.Repeatability and interferenceIn order to prove the precision and practicability of the pre-pared modified electrode,the reproducibility of the Bi2WO6/CPE was investigated.The fabrication reproducibility for six Bi2WO6/ CPEs was carried out by comparing their currents in pH6.0PBS containing0.5l M DES and0.5l M BPA.The relative standard devi-ation(RSD)was 3.5%for DES(n=6)and 4.1%for BPA(n=6), respectively,revealing an excellent reproducibility of the electrode preparation procedure.The electrode retained92%of its initial peak current response after it was kept in refrigerator at4°C in pH6.0PBS for two weeks,which shows long-term stability of the Bi2WO6/CPE surface.Furthermore,the influence of common interfering species on simultaneous determination of DES and BPA in the presence of 0.5l M DES and0.5l M BPA was evaluated.The interference test was performed in the presence of100-fold concentration of glu-cose,Mg2+,Zn2+,Ca2+,K+,Cu2+,Fe3+,Al3+,ClÀ,SO42À,NO3À,10-foldDPV curves on the Bi2WO6/CPE in0.1M pH6.0PBS(A)containing different concentrations of DES(1–17:0,0.02,0.04,0.06,0.08,0.1,0.3,0.5,0.7,0.9,1.1,1.3,2.1,2.3l M).Inset:the calibration plot of the oxidation peak current against the concentration of DES.(B)Containing different concentrations of BPA(1–11:0,0.03,0.09,0.3,0.5,0.7,0.9,1.1,1.3l M).Inset:the calibration plot of the oxidation peak current against the concentration of BPA.5.DPV curves on the Bi2WO6/CPE in0.1M pH6.0PBS(A)containing0.5l M BPA and different concentrations of DES(1–13:0,0.05,0.1,0.2,0.3,0.4,0.6,0.8,1.0,1.2,2.1l M).Inset:the calibration plot of the oxidation peak current against the concentration of DES.(B)Containing0.5l M DES and different concentrations of BPA(1–9:0.1,0.3,0.5,0.7,0.9,1.1,1.3l M).Inset:the calibration plot of the oxidation peak current against the concentration of BPA.Table1Performances of different modified electrodes for the determination of DES or BPA.Modified electrodes Detection range(nM)Detection limit(nM)ReferenceDES BPA DES BPAb-CD-rGO/GCE10–13,000–4–[27] CYP3A4/P(GMA-co-MPC)/AB/GCE200–2800–89–[28] GO–CS/GCE15–30,000–3[17] CS–Fe3O4/GCE–50–30,000–8[18] CS/MNPs-rGO/GCE–60–11,000–16.7[29] Graphene nanofibers–AuNPs/GCE–80–25,000–35[30] Bi2WO6–CPE50–230050–13001520This workconcentration of dopamine,ascorbic acid.These results suggested that lots of species almost have no influence on the signals of them. In addition,20-fold concentration of hydroquinone,hydroxyphe-nol,pyrocatechol and phenol had no influence on the signals of them with deviations below10%.These results suggested that Bi2WO6/CPE has an excellent anti-interference ability for some foreign substances and good selectivity for simultaneous determi-nation of DES and BPA,which might be applied to determine them in practical samples.3.7.Application to samplesIn order to confirm the applicability of the proposed method, the proposed sensor was used to detect DES and BPA in spiked milk samples extracted from milk powder for middle and old age under optimized conditions.A known-amount of the sample solution was added into pH6.0PBS and analyzed by DPV.The results were shown in Table2.As can be observed,the recoveries were in the ranges from90%to99%and88%to98%for DES and BPA,respec-tively,indicating that the sensor might be the potential application of practical samples.4.ConclusionsIn this work,Bi2WO6nanoplates were prepared and success-fully immobilized on CPE by a simple rubbing method to achieve a highly sensitive electrochemical modified electrode for the simultaneous determination of DES and BPA in aqueous solution with a low detection limit.As predicted,the oxidation peak current of DES was enhanced on the modified electrode,and the reasons might be the high specific surface area and unique transfer ability of electrons.Under optimized conditions,the Bi2WO6/CPE showed wider linear behaviors in the range of50–2100nM and 70–1300nM with detection limit of15nM and20nM for DES and BPA,respectively.Finally,the proposed sensor was success-fully applied to the simultaneous determination of DES and BPA in spiked milk samples extracted from milk powder with recover-ies ranging from90%to99%and88%to98%for DES and BPA, respectively.AcknowledgmentsThe authors appreciate the support from the National Natural Science Foundation of China(No.50830303),overall Innovation Project of Science&Technology in Shaanxi Province(No. 2011KTCG03-07),the National Natural Science Foundation of China(51008242),and the Program for Science and Technology Research of Shaanxi Province(No.2012k08-12).Appendix A.Supplementary materialSupplementary data associated with this article can be found,in the online version,at /10.1016/j.jelechem.2014.05.008.References[1]A.C.Gore, D.M.Walker, A.M.Zama, A.E.Armenti,M.Uzumcu,J.Mol.Endocrinol.25(2011)2157–2168.[2]T.A.Hanselman, D.A.Graetz, A.C.Wilkie,Environ.Sci.Technol.37(2003)5471–5478.[3]L.N.Vandenbery,R.Hauser,M.Marcus,N.Olea,W.V.Welshons,Reprod.Toxicol.24(2007)139–177.[4]A.C.Gore,Endocrine-Disrupting Chemicals:From Basic to Clinical Practice,Humdna Press Inc.,New Jersery,2007.[5]H.Sambe,K.Hoshina,K.Hosoya,J.Haginaka,J.Chromatogr.A1134(2006)16–23.[6]T.Lkegami,T.Mukawa,H.Naria,T.Takeuchi,Anal.Chim.Acta504(2004)131–135.[7]Q.W.Yu,Q.Ma,Y.Q.Feng,Talanta84(2011)1019–1025.[8]Y.Wen,B.S.Zhou,Y.Xu,S.W.Jin,Y.Q.Feng,J.Chromatogr.A1133(2006)21–28.[9]C.Liao,K.Kannan,Environ.Sci.Technol.46(2012)5003–5009.[10]Q.Xu,M.Wang,S.Q.Yu,Q.Tao,M.Tang,Analyst136(2011)5030–5037.[11]V.Becena,J.Odermatt,Analyst137(2012)2050–2059.[12]A.Prieto, A.Vallejo,O.Zuloga, A.Schrader, B.Sellergen, E.Schillinger,S.Schrader,M.Moder,Anal.Chim.Acta703(2011)41–51.[13]K.R.Rogers,J.Y.Becker,J.Wang,F.Lu,Field Anal.Chem.Technol.3(1999)161–169.[14]S.Liu,Q.Lin,X.Zhang,X.He,X.Xing,W.Lian,J.Li,M.Cui,J.Huang,Sens.Actuators,B166–167(2012)562–568.[15]Y.Zhang,L.T.Wang,D.B.Lu,X.Z.Shi,C.M.Wang,X.J.Duan,Electrochim.Acta80(2012)77–83.[16]J.J.Fei,X.Q.Wen,L.H.Yi,F.Ge,Y.Zhang,M.H.Huang,X.M.Chen,J.Appl.Electrochem.38(2008)1527–1533.[17]C.M.Yu,W.Y.Ji,Y.D.Wang,N.Bao,H.Y.Gu,Nanotechnology24(2013)115502–115511.[18]C.M.Yu,L.Gou,X.H.Zhou,N.Bao,H.Y.Gu,Electrochim.Acta56(2011)9056–9063.[19]H.S.Yin,Y.L.Zhou,S.Y.Ai,J.Electroanal.Chem.626(2009)80–88.[20]S.Y.Dong,N.Li,G.C.Suo,T.L.Huang,Anal.Chem.85(2013)11739–11746.[21]C.Zhang,Y.F.Zhu,Chem.Mater.17(2005)3537–3545.[22]D.K.Ma,S.M.Huang,W.X.Chen,S.W.Hu,F.F.Shi,K.L.Fan,J.Phys.Chem.C113(2009)4369–4374.[23]Q.L.Sheng,H.Yu,J.B.Zheng,Electrochim.Acta52(2007)4506–4512.[24]F.Giroud,K.Gorgy,C.Gondran,S.Cosnier,D.G.Pinacho,M.P.Marco, F.J.Sánchez-Baez,Anal.Chem.81(2009)8405–8409.[25]H.M.Nassef,L.Civit,A.Fragoso,C.K.O’Sullivan,Anal.Chem.81(2009)5299–5307.[26]A.J.Bard,L.R.Faulkner,Electrochemical Methods:Fundamentals Application,second ed.,Wiley,New York,1980.[27]S.H.Zhang,K.B.Wu,S.S.Hu,Talanta58(2002)747–754.[28]D.Lu,S.X.Lin,L.T.Wang,X.Z.Shi,C.M.Wang,Y.Zhang,Electrochim.Acta85(2012)131–138.[29]Y.X.Zhang,Y.X.Cheng,Y.Y.Zhou,B.Y.Li,W.Gu,Y.Z.Xian,Talanta107(2013)211–218.[30]G.F.Pereira,L.S.Andrade,R.C.Rocha,N.Bochi,S.R.Biaggir,Electrochim.Acta82(2012)3–8.Table2Determination of DES and BPA in spiked milk samples.Component Added(nM)Found(nM)Recovery(%)Sample1DES1009999BPA1009090Sample2DES1008787BPA1009898Sample3DES1009191BPA100888820L.Peng et al./Journal of Electroanalytical Chemistry726(2014)15–20。

一类具有扩散的捕食-食饵模型正解的存在性和惟一性

一类具有扩散的捕食-食饵模型正解的存在性和惟一性

关键词: 捕食 一 食饵;扩散;分歧;惟一性 .
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1 引言
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的存在 性.文 献 f 进 一步 讨论 了该类 模 型,得到 了正解 存 在的 充分条 件,并在 一维情 况 下 3 1 给 出 了正解 的惟 一性 . 目前,对 于带 B D反 应项 的捕食 一 — 食饵 模型 的研 究 已有一些 工作 .文 献 f 利 用特征值 4 ] 变 分原理 得 到 了正 解存 在惟 一 的充分条 件 ,但是 此条 件 比较复 杂 ,实现 起来 比较 困难.将参 数 a限制在 一 定的范 围 内,文 献 f 利 用分歧 理论 给 出了正解 的 整体分 歧结构 .文 献 【 讨 5 ] 6 ] 论 了 m 或 充分大 的情况 ,给 出了正解 的 多重性 和惟一性 . 齐次 N u n 在 e ma n边界条 件下 , 文 献 『 利用 度理论 得 到了非 常数 正解 的存在性 . 7 1 本 文主 要研 究方程 () 1 正解 的存在 性和 惟一性 . 首 先给 出一些 预 备 知识 . 固定 ( i 0 记 X 一 { ∈ C 。 ) ( )= 0 t> , “ 抖 ( : .z ∈ 【 . 2 } 定 义 中的范 数 为通 常 的 B n c a ah空 间 c + ( “ )中的 范数 ,则 是 B n c 空间 .记 a ah P={ ∈X : ( ) , ∈f O ux >0 t u<0 z∈o , P 为 中的 正锥 .对 任意 qx ∈C“f) ; , a}则 () ( , t 令 lq < () 入 () … 是 特征 值问题 () 2q 3q △ +qz = ,X∈Q, = 0 () , ∈ Q 的全部特 征值 . 由文献 [ 知 ,A () 8 1 q 是简 单的, 且 1q 关于 q 格 单调递 增 . () 严 因此 当 q q l 2 且 q ≠ q , 1q)< ( ) 为方便起 见,简记 () l 2时 (1 1g . 2 0 为 .不妨设 l 0为 主特征 值 >

Uniqueness of steady states for a certain chemical reaction

Uniqueness of steady states for a certain chemical reaction

a r X i v :q -b i o /0512046v 1 [q -b i o .M N ] 28 D ec 2005Uniqueness of steady states for a certain chemical reactionLiming Wang and Eduardo SontagDepartment of Mathematics,Rutgers UniversityIn [1],Samoilov,Plyasunov,and Arkin provide an example of a chemical reaction whose full stochastic (Master Equation)model exhibits bistable behavior,but for which the deterministic (mean field)version has a unique steady state.The reaction that they provide consists of an enzymatic futile mechanism driven by a second reaction which induces “deterministic noise”on the concentration of the forward enzyme (through a somewhat artificial activation and deactivation of this enzyme).The model is as follows:N +N k 1−→←−k −1N +E N k 2−→←−k −2E S +E k 3−→←−k −3C 1k 4−→P +E P +F k 5−→←−k −5C 2k 6−→S +F .Actually,[1]does not prove mathematically that this reaction’s deterministic model has a single-steady state property,but shows numerically that,for a particular value of the kinetic constants k i ,a unique steady state (subject to stoichiometric constraints)exists.In this short note,we provide a proof of uniqueness valid for all possible parameter values.We use lower case letters n,e,s,c 1,p,c 2,f to denote the concentrations of the corresponding chemicals,as functions of t .The differential equations are,then,as follows:n ′=−k 1n 2+k −1ne −k 2n +k −2e e ′=−k 3se +k −3c 1+k 4c 1+k 1n 2−k −1ne +k 2n −k −2e s ′=−k 3se +k −3c 1+k 6c 2c ′1=k 3se −k −3c 1−k 4c 1p ′=k 4c 1−k 5pf +k −5c 2c ′2=k 5pf −k −5c 2−k 6c 2f ′=−k 5pf +k −5c 2+k 6c 2.Observe that we have the following conservation laws:e +n +c 1≡α,f +c 2≡β,s +c 1+c 2+p ≡γ.Lemma 1.For each positive α,β,γ,there is a unique (positive)steady state,subject to the conservation laws.Proof.Existence follows from the Brower fixed point theorem,since the reduced system evolves on a compact convex set (intersection of the positive orthant and the affine subspace given by the stoichiometry class).We now fix one stoichiometry class and prove uniqueness.Let ¯n ,¯e ,¯s ,¯c 1,¯p ,¯c 2,¯fbe any steady state.From dn/dt=0,we obtain that:k1¯n2+k2¯n¯e=.k3¯eSolving dc2/dt=0for p and then substituting f=β−c2gives:(k−5+k6)¯c2¯p=¯c1.k6The derivative of¯e with respect to¯n is:k1k−1¯n2+2k1k−2¯n+k2k−2。

Simultaneous determination of phenolic acids and 2,4-dihydroxy-7-

Simultaneous determination of phenolic acids and 2,4-dihydroxy-7-

Journal of Chromatography A,864(1999)315–321/locate/chromaSimultaneous determination of phenolic acids and 2,4-dihydroxy-7-methoxy-1,4-benzoxazin-3-one in wheat (Triticum aestivum L.)bygas chromatography–tandem mass spectrometrya ,a ab c*Hanwen Wu ,Terry Haig ,Jim Pratley ,Deirdre Lemerle ,Min AnaFarrer Centre for Conservation Farming ,Charles Sturt University ,P .O .Box 588,Wagga Wagga ,NSW 2678,AustraliabNSW Agriculture ,Wagga Agricultural Institute ,Wagga Wagga ,NSW 2650,AustraliacEnvironmental and Analytical Laboratories ,Charles Sturt University ,P .O .Box 588,Wagga Wagga ,NSW 2678,AustraliaReceived 23June 1999;received in revised form 24September 1999;accepted 27September 1999AbstractA procedure using gas chromatography and tandem mass spectrometry (GC–MS–MS)has been developed for the identification and quantification of some allelochemicals in wheat (Triticum aestivum L.).The quantities of allelochemicals in wheat shoots ranged from 2.9to 110mg per kilogram of dry shoot pared with gas chromatography–mass spectrometry (GC–MS),the GC–MS–MS technique significantly increased instrument selectivity and sensitivity,thereby providing more reliable quantitation results in the determination of the phytotoxic compounds examined during this allelopathy research.©1999Elsevier Science B.V .All rights reserved.Keywords :Wheat;Allelochemicals;Triticum aestivum ;Phenolic acids;Dihydroxymethoxybenzoxazinone1.Introductionbeen regarded as some of the major phenolic acids predominantly identified in wheat stubbles and in the Wheat (Triticum aestivum L.)has been found to soil [1,5].In addition to the phenolic acids,one of possess allelopathic potential [1,2]and studies have the hydroxamic acids,2,4-dihydroxy-7-methoxy-1,4-been conducted to apply wheat allelopathy for benzoxazin-3-one (DIMBOA),has also been re-biological weed control [3,4].Wheat cultivars dif-ported as an active allelochemical in wheat [6].The fered in their allelopathic ability to suppress the phytotoxicity of these compounds has been clearly growth of annual ryegrass (Lolium rigidum G.)and demonstrated [7,8].the degree of allelopathic inhibition was highly Allelopathic compounds are often found as com-associated with the total phenolic contents contained plex mixtures and their determination presents an in each wheat extract [4].p -Hydroxybenzoic,van-analytical challenge.Many traditional separation illic,p -coumaric,syringic and ferulic acids havetechniques such as paper,thin-layer,and column chromatography have been used for the separation and identification of phenolic compounds,but these *Corresponding author.Tel.:161-2-6933-2749;fax:161-2-6933-methods are limited in separation power [9].High-2812.E -mail address :11134425@.au (H.Wu)performance liquid chromatography (HPLC)gives0021-9673/99/$–see front matter ©1999Elsevier Science B.V .All rights reserved.PII:S0021-9673(99)01034-1316H.Wu et al./J.Chromatogr.A864(1999)315–321better results and has been widely used for the ence and the GC-grade diethyl ether was purchased analysis of phenolics and DIMBOA in plants from BDH.The derivatising reagent,N-methyl-N-[5,7,10].The best separation power has been(trimethylsilyl)trifluoroacetamide(MSTFA),was ob-achieved by capillary gas chromatography(GC)in tained from Alltech Australia.the determination of phenolic mixtures[9].Gaschromatography coupled with mass spectrometry 2.2.Analytical procedure(GC–MS)has been regarded as a powerful ana-lytical tool for the characterisation of complex 2.2.1.Preparation of calibration standards organic mixtures and has successfully been em-Seven standard solutions each containing all six ployed in the identification and quantitation of active target compounds,i.e.,p-hydroxybenzoic acid,van-allelopathic compounds in vulpia(Vulpia myuros L.illic acid,syringic acid,p-coumaric acid,ferulic acid Gmel)[11].Recent advances in instrumentation have and DIMBOA,werefirst prepared in methanol at further boosted the analytical power for the de-concentrations of0.05,0.1,0.5,1,5,10,20m g/ml, termination of allelopathic compounds.Ion trap respectively.In separate analyses,1ml from each of detectors have been improved to perform tandem the seven methanolic standard solutions was pipetted mass spectrometry(MS–MS),which enables the ion into a2-ml minivial and dried by nitrogen blow-trap to isolate an ion of interest and then produce down.A1-ml volume of internal standard p-chloro-characteristic progeny ions by collision-induced dis-benzoic acid at the concentration of5m g/ml in sociation(CID).Compared to single-stage MS,MS–methanol was then pipetted into the dry minivial and MS technology enhances instrumental selectivity and dried again with nitrogen prior to the derivatisation sensitivity and has become a favoured tool for the step.quantitative analysis of the complex matrixes en-countered in biological and environmental applica- 2.2.2.Preparation of wheat samplestions[12].However,this powerful technique has not Surface-sterilised and pre-germinated wheat seeds yet been much employed in allelopathy studies.(Triticum aestivum,cv.Triller)were grown in a Although both phenolic acids and cyclic hydrox-nutrient-free agar medium under aseptic conditions amic acids have been reported in relation to wheat in a controlled growth cabinet with a daily light/dark allelopathy,no attempt has been made to simul-cycle of13h/11h and a temperature cycle at taneously determine these two distinct groups of258C/138C.Thefluorescent light intensity in the3allelopathic compounds.This study was designed to cabinet was3.5660.16?10lux.Shoots of17-day-apply gas chromatography–tandem mass spec-old wheat seedlings were harvested and immediately trometry(GC–MS–MS)to selectively identify and freeze-dried(Christ Alpha1-4freeze dryer,B.Braun quantify some phenolic acids and DIMBOA in a Biotech International).An amount of0.100g of very complex matrix of wheat shoot extract.freeze-dried wheat shoots was cut into2-mm lengths,ground into powder with a mortar and pestle after theaddition of liquid nitrogen and macerated with3ml 2.Experimental of0.001M HCl.The entire macerate was transferredinto a labelled glass scintillation vial and sonicated at 2.1.Chemicals and reagents58C for15min(Unisonics,Australia).The resultingmixture was centrifuged at20000rpm at108C for p-Hydroxybenzoic acid(PHB),vanillic acid15min to remove the debris(Avanti J-30I Cen-(V AN),syringic acid(SYR),p-coumaric acid trifuge,Beckman,USA).The supernatant was then (COU),ferulic acid(FER)and the internal standard collected and extracted three times with10-ml (p-chlorobenzoic acid)were obtained from Sigma–portions of diethyl ether.The ether layers were Aldrich.DIMBOA was kindly provided by bined and evaporated on a rotary evaporator William S.Chilton of the Department of Botany,under reduced pressure at358C until the volume of North Carolina State University,Raleigh,NC,USA.residual solution was approximately2ml.The2ml HPLC-grade methanol was obtained from EM Sci-ether solution was then transferred to a2-ml minivialH.Wu et al./J.Chromatogr.A864(1999)315–321317 and dried with nitrogen blow-down.A1-ml volume99.9999%and its linear velocity was34cm/s. of internal standard p-chlorobenzoic acid at the Injector temperature was maintained at2808C,and concentration of5m g/ml in methanol was then the injection volume was1m l with the splitless pipetted into the dry minivial and dried again with mode.nitrogen prior to the derivatisation step.The electron impact ionization(EI)mode withautomatic gain control(AGC)was used for MS.The 2.2.3.Derivatisation electron multiplier voltage for MS–MS was1450V, The silylation of calibration standards and the AGC target was10000counts andfilament emission wheat shoot sample was accomplished by the addi-current was60m A with the axial modulation am-tion of1.00ml of MSTFA at608C for30min.The plitude at4.0V.The ion trap was held at2008C and silylated samples were analysed by GC–MS–MS or the transfer line at2508C.Manifold temperature was GC–MS.The large excess of MSTFA ensured that set at608C.Mass spectral scan time from m/z50to the derivatization was complete.Care was taken to450was 1.0s(using3microscans).Nonresonant ensure anhydrous conditions during the preparation CID was used for MS–MS.The associated parame-and derivatization process because of the high sen-ters for the MS–MS method were optimised for each sitivity of trimethylsilyl(TMS)derivatives towards individual compound(Table1).The method was moisture.divided into10acquisition segments so that differention preparationfiles could be used to optimise the 2.2.4.GC–MS–MS instrumentation and conditions conditions for the TMS derivatives of the chemically GC–MS–MS analysis was carried out on a Varian distinct internal standard,phenolic acids and DIM-3400CX gas chromatograph coupled with a Varian BOA.Standard samples of both p-coumaric acid and Saturn2000ion trap mass spectrometer.Samples ferulic acid consisted of trans and cis isomers so that were introduced via a DB-5MSITD(Ion Trap four segments were required to characterise the p-Tested)fused-silica capillary column of30m30.25coumaric and ferulic acids.Thefirst segment was a mm I.D.,with a stationary phase thickness of0.259-min solvent delay,which was necessary for the m m(J&W Scientific,Alltech,Australia).The gas protection of the electron multiplier from the large chromatographic conditions for the analysis of wheat solvent peak signal.allelochemicals were slightly modified from An[7].The column temperature was initially held at808C 2.2.5.Identification and quantitationfor1min,then programmed to1608C at a rate of Two user libraries(MS and MS–MS library)were 108C/min,from160to2358C at a rate of58C/min generated with the injection of TMS-derivatised and from235to2808C at a rate of508C/min,with a authentic reference compounds by GC–MS or GC–final hold time of5min(total run time,29.9min).MS–MS analysis.The MS library recorded the Helium was used as the carrier gas with purity of retention times and the mass spectra of TMS deriva-Table1aIon trap MS–MS method parametersbAcquisition segment2345678910 Compound(silylated)p-Chlorobenzoic acid PHB V AN cis-COU SYR cis-FER trans-COU DIMBOA trans-FER Segment time(min) 4.100.40 2.60 2.000.300.50 1.10 1.808.10 Retention time(min)9.7813.3015.7416.2318.2318.6319.0620.1621.91 Chosen precursor ion(m/z)213267297293297323293340323 Excitation amplitude(V)546443.64543.6414546.541.2 Excitation storage level(m/z)608065656565657565 Quantifying product ion(m/z)169223267249253293249194293a Mass isolation window(m/z)was set at3and excitation time(ms)at20.b Segment one was the solvent delay.318H.Wu et al./J.Chromatogr.A864(1999)315–321tives of authentic standards under the chosen chro-acid,p-hydroxybenzoic acid,vanillic acid,syringic matographic conditions.Similarly,the MS–MS li-acid,p-coumaric acid,ferulic acid and DIMBOA by brary recorded the retention times and the daughter comparing retention times and the mass spectra with mass spectra derived from the specific precursor ions those of TMS derivatives of their authentic com-of TMS derivatives of each authentic standard after pounds under identical conditions.However,the p-CID with helium gas.The allelopathic substances hydroxybenzoic acid,cis-p-coumaric acid,trans-p-were then identified by comparing retention times coumaric acid,syringic acid,cis-ferulic acid and and mass spectral data with those in either user DIMBOA were strongly coeluted with background library,depending upon the type of analysis.All substances(Fig.2),although p-chlorobenzoic acid, quantitation was performed by the method of internal vanillic acid and trans-ferulic acid were well sepa-standardisation using p-chlorobenzoic acid at a rated.Owing to the complexity of the sample matrix, concentration of5m g/ml as the internal standard.for each of the six co-eluted analytes shown in Fig. The quantitation of these compounds was based on2,there could not be found unique characteristic the peak area of the selected daughter ions listed in GC–MS ions of sufficient intensity to serve as Table1and is reported in units of milligrams per suitable quantifying ions.In order to help illustrate kilogram of dry matter.All calibration standards and this difficult background matrix problem,the more the wheat samples were run in triplicate.characteristic analyte ion chromatograms and totalion chromatograms of Fig.2have been sup-plemented with indicative background ion chromato-3.Results and discussion grams from coelutants.Coelution with these analytesis also further evident in the asymmetry of the more Underivatised phenolic acids and DIMBOA have characteristic analyte ion profiles.The simple GC–relatively low volatility and are not suitable for direct MS results were therefore not considered adequate capillary GC analysis.MSTFA was chosen as the for accurate quantitation.derivatisation reagent to convert analytes into vola-The tandem mass spectrometry technique was tile compounds.The GC–MS analysis of silylated introduced in order tofilter out unwanted chemical wheat shoot extract was repeated three times(Fig.backgrounds.After preliminary experimentation,the 1).Analysis by GC–MS was able to identify all the MS–MS conditions shown in Table1were used to target allelopathic compounds,i.e.,p-chlorobenzoic analyse the phenolic acids and DIMBOA in wheatFig. 1.Reconstructed total ion current chromatogram(RTIC)of derivatized wheat shoot extract obtained from GC–MS.Peaks: 15p-chlorobenzoic acid,25p-hydroxybenzoic acid,35vanillic acid,45cis-p-coumaric acid,55syringic acid,65cis-ferulic acid,75trans-p-coumaric acid,852,4,-dihydroxy-7-methoxy-1,4,-benzoxazin-3-one,95trans-ferulic acid.H.Wu et al./J.Chromatogr.A864(1999)315–321319Fig.2.GC–MS run showing the coelution of analytes with background signals(*:analytes were identified by comparing retention times and mass spectral data with those in the user MS library;a:precursor ion of the analyte;b:background ion).shoots.The GC–MS–MS analysis of the shoot compounds were much lower in GC–MS than in extract was repeated three times.A highly-resolved GC–MS–MS(Table3).The signal/noise ratios for chromatogram was successfully obtained(Fig.3).p-chlorobenzoic acid,p-hydroxybenzoic acid and The MS–MS technique successfully removed most vanillic acid in the shoot sample were51,25and29 of the unwanted chemical signals and provided a times higher under MS–MS conditions than under clear background for the quantification of the chosen MS conditions.This technique was then employed to allelopathic compounds.The precursor ion of the quantify the allelochemicals in wheat(Table2). particular compound was isolated and then CID with Wheat shoots contained a higher amount of DIM-helium carrier gas gave rise to a characteristic BOA than of phenolic acids.The allelochemical daughter mass spectrum for each analyte(Table2).contents in wheat shoots were110mg/kg dry mass The preferential isolation of the particular ions by the for DIMBOA and2.9mg/kg dry mass for cis-p-MS–MS technique yielded much stronger analyte coumaric acid.The difficulties in the separation and signals than those of single stage MS analysis,identification of cis and trans mixtures have been thereby significantly reducing the effect of matrix reported[13].However,the cis and trans isomers of noise.The signal/noise ratios for all the allelopathic p-coumaric and ferulic acids were successfully sepa-320H.Wu et al./J.Chromatogr.A864(1999)315–321Fig.3.Reconstructed total ion current chromatogram of derivatized wheat shoot extract obtained from GC–MS–MS.Peaks as in Fig.1. Table2Important ions present in the daughter mass spectra of silylated compounds in wheat extract by GC–MS–MS and their concentrations aPeak pound m/z Quantity6SD(mg/kg dry mass)b1p-Chlorobenzoic acid213,169(100%),141,138,133,131,105,91,75Internal standard2PHB267,251,225,223(100%),207,193,179,147,1032262.33V AN297,267(100%),253,237,225,224,223,181,1475664.34cis-p-COU293,251,249(100%),247,233,231,223,219,203 2.960.15SYR297,271,255,253(100%),225,223,193,179,1331160.76cis-FER323,294,293(100%),279,264,249,233,179,175 3.960.27trans-p-COU293,251,249(100%),247,233,231,223,219,2033761.58DIMBOA340,296,268,250,221,220,194(100%),192,14711064.89trans-FER323,294,293(100%),279,264,249,233,179,1758962.0a Identified as trimethylsilyl(TMS)derivative.b Thefirst ion in each compound list is the precursor ion;all other ions are greater than5%of the base peak.rated under the present chromatographic conditions Table3despite their similar daughter mass spectra(Table2). Signal/noise ratio of GC–MS and GC–MS–MSResults showed that trans-ferulic and trans-p-Compound Signal/noise ratio6SDcoumaric acid were present in higher quantities than GC–MS GC–MS–MS their cis isomers in wheat shoots.p-Chlorobenzoic acid3469.61700652.8PHB1162.2270649.1V AN8867.72500638.0 4.Conclusionscis-p-COU2463.52662.1SYR1365.76865.0Application of state-of-the-art analytical tools can cis-FER1767.34264.1trans-p-COU1769.3180614.1generate unambiguous results in the determination of DIMBOA 3.362.31763.0responsible allelopathic compounds in a complex trans-FER35611.0250617.2mixture of plant origin.In the present study,aH.Wu et al./J.Chromatogr.A864(1999)315–321321 GC–MS–MS technique has been successfully used provision of GC–MS–MS instrumentation from the to obtain a highly resolved chromatogram to de-Environmental and Analytical Laboratories at termine several key phenolic compounds and DIM-Charles Sturt University.BOA.The enhanced sensitivity and selectivity ofGC–MS–MS have provided reliable quantitativeresults for the biologically active compounds in Referencescomplex mixtures encountered in this allelopathyresearch and can be employed to screen cultivars for[1]W.D.Guenzi,T.M.McCalla,Agron.J.58(1966)303.[2]R.W.L.Kimber,Aust.J.Agric.Res.18(1967)361.their differential production of allelopathic com-[3]J.A.Spruell,Dissertation Abstr.Int.,B Sci.Eng.45(1984) pounds in a large number of wheat accessions.This1102B.technique coupled with DNA technology will facili-[4]H.Wu,J.Pratley,D.Lemerle,T.Haig,B.Verbeek,in:Proc. tate the identification of genetic markers conferring9th Aust.Agron.Conf.,Wagga Wagga,1998,p.567.the biosynthesis of allelopathic compounds.The[5]U.Blum,T.R.Wentworth,K.Klein,A.D.Worsham,L.D.King,T.M.Gerig,S.W.Lyu,J.Chem.Ecol.17(1991)1045. possibilities for genetic manipulation of crop al-[6]H.M.Niemeyer,Phytochemistry27(1988)3349. lelopathic potential have been reviewed[14].The[7]M.An,Ph.D.Thesis,Charles Sturt University(1995). genetic manipulation of crop cultivars might provide[8]F.J.Perez,Phytochemistry29(1990)773.crop plants with strong allelopathic potential to[9]C.S.Creaser,M.R.Koupai-Abyazani,G.R.Stephenson,J. compete with weeds,thereby reducing the input of Chromatogr.478(1989)415.[10]F.J.Perez,J.Ormeno-Nunez,J.Chem.Ecol.17(1991) herbicides into agroecosystems.1037.[11]M.An,J.E.Pratley,T.Haig,Rapid Commun.Mass Spec-trom.10(1996)104.Acknowledgements[12]C.K.Van Pelt,H.Haggarty,J.T.Brenna,Anal.Chem.70(1998)4369.[13]E.M.Gaspar,H.C.Neves,Allelopathy J.2(1995)79. The authors are thankful forfinancial support from[14]H.Wu,J.Pratley,D.Lemerle,T.Haig,Weed Res.39(1999) the Australian Cooperative Research Centre for171.Weed Management Systems and acknowledge the。

高效液相色谱_荧光法测定小鼠脑组织中的单胺类神经递质

高效液相色谱_荧光法测定小鼠脑组织中的单胺类神经递质

·774· ◇调查与分析 ◇
安徽医科大学学报 A cta U n iversita tis M ed icina lis A nhu i 2009 Dec; 44 (6)
急性白血病 1 185例次住院患者血流感染特点及危险因素分析
秦 慧 ,杨明珍 ,宋万灯 ,武琳琳 ,缪华伟 ,程 歆 ,吴 炜 ,刘沁华 ,王永庆
安徽医科大学学报 A cta U n iversita tis M ed icina lis A nhu i 2009 Dec; 44 (6)
·773·
1. 4 统计学处理 数据结果以 x ±s表示 ,采用线 性回归最小二乘法计算单胺类神经递质的标准曲 线。
2 结果
2. 1 标准色谱图 实验得到各标准物质谱图见图 1, 3种标准物质都达到了基线分离 。得到了小鼠脑 组织匀浆样品的色谱图 (图 2) ,除了多巴胺前有一 大的未知峰与多巴胺未达到基线分离外 ,其余各种 化合物均达到基线分离 。标准液和脑匀浆样品中的 NE、DA 和 52HT的峰之间分离较好 (样品中 DA 与 杂质峰的分离尚有待改善 ) 。
相关系数 0. 999 7 0. 999 9 0. 998 9
2. 3 回 收率 和精 密度 的测 定 按 113 操 作 , 按 0110 g脑 (湿重 )加入 110 m l的比例加入低 、中 、高 浓度的标准溶液 ,于同日内分别测定 NE、DA 和 52 HT加入量的对照品脑组织匀浆样品 ,每种加入量样 品平行测定 5次 ,计算各种标准物不同浓度的脑组 织匀浆样品回收率 ,结果如表 3。连续测定混合标 准液 5次 , NE、DA 和 52HT的峰面积日内测定的相 对标准偏差分别为 217%、215%和 314%。
图 1 3种神经递质混合标准溶液色谱图 (1: NE; 2: DA; 3: 52HT)

Simultaneous determination of multi-mycotoxins in

Simultaneous determination of multi-mycotoxins in

This article was downloaded by: [University of Jiangnan]On: 23 December 2014, At: 22:26Publisher: Taylor & FrancisInforma Ltd Registered in England and Wales Registered Number: 1072954 Registered office: Mortimer House,37-41 Mortimer Street, London W1T 3JH, UKClick for updatesFood Additives & Contaminants: Part APublication details, including instructions for authors and subscription information:/loi/tfac20Simultaneous determination of multi-mycotoxins in palm kernel cake (PKC) using liquid chromatography-tandem mass spectrometry (LC-MS/MS)S. Yibadatihan ab, S. Jinap ab& N. A MahyudinaaFood Safety Research Centre (FOSREC), Faculty of Food Science and T echnology , Universiti Putra Malaysia, Serdang, MalaysiabInstitute of Tropical Agriculture, Universiti Putra Malaysia, Serdang, MalaysiaAccepted author version posted online: 14 Nov 2014.Published online: 17 Nov 2014.PLEASE SCROLL DOWN FOR ARTICLESimultaneous determination of multi-mycotoxins in palm kernel cake (PKC)using liquid chromatography-tandem mass spectrometry (LC-MS/MS)S.Yibadatihan a,b ,S.Jinap a,b *and N.A Mahyudin aa Food Safety Research Centre (FOSREC),Faculty of Food Science and Technology,Universiti Putra Malaysia,Serdang,Malaysia;bInstitute of Tropical Agriculture,Universiti Putra Malaysia,Serdang,Malaysia(Received 8July 2014;accepted 13October 2014)Palm kernel cake (PKC)is a useful source of protein and energy for livestock.Recently,it has been used as an ingredient in poultry feed.Mycotoxin contamination of PKC due to inappropriate handling during production and storage has increased public concern about economic losses and health risks for poultry and humans.This concern has accentuated the need for the evaluation of mycotoxins in PKC.Furthermore,a method for quantifying mycotoxins in PKC has so far not been established.The aims of this study were therefore (1)to develop a method for the simultaneous determination of mycotoxins in PKC and (2)to validate and verify the method.A liquid chromatography-tandem mass spectrometry (LC-MS/MS)method using an electrospray ionisation interface (ESI)in both positive-and negative-ion modes was developed for the simultaneous determination of a flatoxins (AFB 1,AFB 2,AFG 1and AFG 2),ochratoxin A (OTA),zearalenone (ZEA),deoxynivalenol (DON),fumonisins (FB 1and FB 2),T-2and HT-2toxin in PKC.An optimum method using a 0.2ml min –1flow rate,0.2%formic acid in aqueous phase,10%organic phase at the beginning and 90%organic phase at the end of the gradient was achieved.The extraction of mycotoxins was performed using a solvent mixture of acetonitrile –water –formic acid (79:20:1,v/v)without further clean-up.The mean recoveries of mycotoxins in spiked PKC samples ranged from 81%to 112%.Limits of detection (LODs)and limits of quanti fication (LOQs)for mycotoxin standards and PKC samples ranged from 0.02to 17.5μg kg −1and from 0.06to 58.0μg kg −1,respectively.Finally,the newly developed method was successfully applied to PKC samples.The results illustrated the fact that the method is ef ficient and accurate for the simultaneous multi-mycotoxin determination in PKC,which can be ideal for routine analysis.Keywords:LC-MS/MS;multi-mycotoxins;palm kernel cake;optimisation;simultaneous determinationIntroductionPalm kernel cake (PKC)is an important oil palm by-product;compared with other feedstuffs its nutritional value and long-term availability make PKC more compe-titive in international feed markets and it has been widely used as a major component of poultry feed ingredients.PKC is produced and stored under unhygienic conditions with uncontrolled temperature and relative humidity,which can promote the formation of mycotoxins.It has been well established that contamination of poultry feeds with mycotoxins may induce sanitary disturbances and mortality among the birds and secondary contamination of the human consumer via eggs,poultry meat and giblets (Shareef 2010).Even the intake of very low levels of mycotoxins can cause overt mycotoxicosis,and also leads to the impairment of the immune system and acquired resistance to infections causing health problems which lead to economic losses in the form of decreased productivity (Krnjaja et al.2008).Mycotoxins are a diverse group of toxic secondary metabolites produced by certain filamentous fungi,mostly of the genera Aspergillus ,Fusarium and Penicillium .Poultry are highly susceptible to mycotoxicoses causedby a flatoxins (AFB 1,AFB 2,AFG 1and AFG 2),ochratoxin A (OTA),zearalenone (ZEA),deoxynivalenol (DON),fumonisins (FB 1and FB 2),and T-2and HT-2toxin (Poornima &Palanisamy 2013).The co-occurrence of different toxic compounds implies a potential risk of addi-tional or even synergistic toxic effects after consumption of contaminated food or feed commodities (Škrbi ćet al.2011).Table 1presents the main health effects and symp-toms of the most predominant mycotoxins.Due to adverse toxicities,evaluation of the mycotoxins in PKC is an essential prerequisite for monitoring and prevention of their potential hazard to poultry and human health and to economic losses.To ensure the safety of the food chain,most countries have set maximum levels of mycotoxins for poultry feed.The European Commission has set limits of 100μg kg −1for total AFs and 20μg kg −1for AFB 1;40μg kg −1for OTA;400μg kg −1for ZEA;200μg kg −1for T-2and HT-2;5000μg kg −1for DON and 20000μg kg −1for fumonisins (FB 1,FB 2)(European Food Safety Authority 2014).To assess the toxicological risks of mycotoxins in humans and animals and to control mycological contamina-tion,analytical methods have been developed to determine*Corresponding author.Emails:jinap@.my ;sjinap@Food Additives &Contaminants:Part A ,2014V ol.31,No.12,2071–2079,/10.1080/19440049.2014.978396©2014Taylor &FrancisD o w n l o a d e d b y [U n i v e r s i t y o f J i a n g n a n ] a t 22:26 23 D e c e m b e r 2014the levels of mycotoxins in various commodities,such as cereals (Rahmani et al.2011;Soleimany,Jinap,Faridah,et al.2012),peanuts (Arzandeh et al.2010;Jinap et al.2012;Hong et al.2010),peppers (Jalili &Jinap 2012),liquorice root (Wang et al.2013),nutmeg (Kong et al.2013),agro-food (Li et al.2013),soybean-based food and feed (Piotrowska et al.2013),milk (Sorensen and Elbak 2005;Muscarella et al.2007),and animal feed (Kolosova &Stroka 2012;Ates et al.2013).However,no method has been developed for the determination of mycotoxins in PKC.Most of the existing mycotoxin determination methods have used either LC-MS/MS (Liao et al.2011;Soleimany,Jinap &Abas 2012;De Girolamo et al.2013;Warth et al.2013)or HPLC with various detectors (Curticapean et al.2011;Soleimany et al.2011;Rahmani et al.2013;Wang et al.2013).The former has gained more popularity than the latter due to the advantages of time and the solvent-saving separa-tion without any pre-or post-column derivatisation.Moreover,due to the high sensitivity and improved speci fi-city of LC-MS/MS methods,we can inject crude sample extracts.Thus,simple and ef ficient sample extraction meth-ods can be developed without applying further clean-up steps during sample preparation instead of using the costly and labour-demanding extraction methods.The impetus of this study was to develop an accurate LC-MS/MS simultaneous multi-analyte method using a simple and ef ficient sample extraction to detect a flatoxins(AFB 1,AFB 2,AFG 1and AFG 2),ochratoxin A (OTA),zearalenone (ZEA),deoxynivalenol (DON),fumonisins (FB 1and FB 2),T-2and HT-2toxins in PKC.To the best of our knowledge,this is the first study report on the simultaneous determination of multi-mycotoxins in PKC.Materials and methodsChemicals and reagentsAnalytical standards of all mycotoxins,including a flatoxins (AFB 1,AFB 2,AFG 1and AFG 2),OTA,DON,ZEA,T-2,HT-2and fumonisins (FB 1,FB 2)were purchased from Sigma-Aldrich (St.Louis,MO,USA).Methanol and for-mic acid,which were used for the preparation of the mobile phase,were LC grade and obtained from Merck (Darmstadt,Germany).All eluents were filtered through 0.22-µm membrane filters (Whatman,Maidstone,UK).Deionised distilled water was obtained from a Milli-Q puri fication system (Bedford,MA,USA).Preparation of stock and working standard solutions To make a stock-standard mixture,3ml of mixed a flatoxins standard solution (AFB 1and AFG 1at 1000ng ml −1;AFB 2,AFG 2at 300ng ml −1)was mixed with 404μl of OTA standard solution (9900ng ml −1),367.7μl of ZEA standardTable mon mycotoxins and their toxicity in poultries (Richard 2007;Nagwa et al.2013).Mycotoxin EffectsSigns/symptomsA flatoxinsHepatotoxic effects Jaundice (yellow skin)Teratogenic effects Higher incidence of cancer in exposed animalsCarcinogenic Weight variation of the internal organs:enlargement of the liver,spleen and kidneysMutagenic Decreased feed intake (anorexia),decreased daily weight gain,decreased slaughtering weight,inhomogeneous flocksImmunosuppressionDecreased resistance to environmental and microbial stressors,increased susceptibility to diseasesOchratoxin AImmunosuppression Decreased resistance to environmental and microbial stressors,increased susceptibility to diseasesCarcinogenicKidney and liver toxin,carcinogen;chronic toxicity as accumulates in body.Trichothecenes(DON,T-2,HT-2)Immunosuppression Decreased resistance to environmental and microbial stressors,increased susceptibility to diseasesDecreased performance Reduced feed intake,reduced weight gain,impaired feed conversion ratio (FCR),feed refusal,inhomogeneous flocks Dermal toxicityOral and dermal lesionsHematopoietic effectsHaemorrhages (stomach,heart,intestine,lung,bladder and kidney),blood pattern disorders Digestive disorders Diarrhoea,vomitingZearalenone Estrogenic effects Enhanced secondary sex characteristics,enlargement of uterus and mammary glandsReproductive effects Atrophy of testicles and ovaries,abortion,infertility Fumonisins(FB 1and FB 2)Decreased performance Reduced weight gain,impaired FCRPathological changesIncreased kidney and liver weight,liver necrosis2072S.Yibadatihan et al .D o w n l o a d e d b y [U n i v e r s i t y o f J i a n g n a n ] a t 22:26 23 D e c e m b e r 2014solution (108810ng ml −1),520μl of DON standard solution (96160ng ml −1),1086.7μl of FB 1standard solution (46000ng ml −1),882μl of FB 2standard solution (56700ng ml −1),97.3μl of T-2toxin standard solution (102640ng ml −1),and 100μl of HT-2toxin standard solution (99900ng ml −1)in a 10-ml volumetric flask and filled to volume with methanol to achieve a mix stock solu-tion of AFB 1,AFB 2,AFG 1,AFG 2,OTA,ZEA,FB 1,FB 2,T-2toxin,HT-2toxin and DON at concentrations of 300,90,300,90,400,4000,5000,5000,1000,1000and 5000ng ml −1,respectively.The working standard solutions were prepared by diluting this stock standard mixture with methanol at different concentration ranges,which are given in Table 3.All stock and working standard solutions were stored in amber vials and kept in a freezer at –20°C.EquipmentThe following apparatuses were used for preparing standard solutions and sample extractions:adjustable pipettes (Gilson Pipetman L,Paris,France);a V ortex-mixer (Harmony,Tokyo,Japan),1204Buhler mill (Buhler S.P.A.,Milan,Italy);a Recipro shaker (Jeio teck,Korea);a centrifuge (KUBOTA 2100,Tokyo,Japan);and a nitrogen evaporator with a heated block (N-EV AP ,Organomation Associates,Inc.,Berlin,MA,USA).LC-MS/MS systemLC analysis was performed using a Finnegan TSQ quan-tum ultra -mass (Thermo Fisher Scienti fic,San Francisco,CA,USA)system consisting of a binary pump,a degasser,a column oven and an autosampler.The MS system was operated with an ESI method in both positive-and nega-tive-ion modes using nitrogen spray gas.The capillary voltage was 3kV;the source and desolation temperatures were set at 120and 350°C,respectively.A 25-μl sample was injected on a reverse-phase symme-try C18column (2.00×150mm,3μm particles)with a column temperature of 30°C.To achieve the optimal chro-matographic separation of all the analytes,different types of mobile phase compositions with different proportions were investigated,such as 5–25%and 70–90%methanol or acet-onitrile at the beginning and end of the gradient,respectively,and different acid types,including 0–0.7%formic acid and acetic acid.Different flow rates (150–350μl min −1)and injection volumes (5–25μl)were also tested.The mobile phase solutions were filtered through a 0.22μm membrane and ultrasonically degassed prior to application.Sample and sample preparationA total of 25PKC samples were collected from different locations of Malaysia between February and June 2013.The samples were kept in a dark,cool room at 4°C untilanalysis.Then,5g of the ground PKC sample were homogenised with 20ml of the organic extraction solvent mixture of acetonitrile –water –formic acid (79:20:1v/v)by shaking for 60min on a Recipro shaker.The supernatant was then centrifuged at 3000rpm for 10min in a Centrifuge2W/E3as described by Soleimany et al.(2011).Next,1ml of the final extract from the one-step extraction was diluted with 3ml water,passed through a 0.45-μm filter and injected into the LC-MS/MS (Spanjer et al.2008;Herebian et al.2009;Zachariasova et al.2010).The purpose of sample dilution during the sample preparation procedure was to reduce the possible matrix effect (Patel 2011).Method validationValidation of the LC-MS/MS method was carried out by investigating the basic performance characteristics included linearity,LODs,LOQs,recovery and precision in accordance with the European Commission regulation for the performance of analytical methods (EC 657/2002).LinearityLinear regression analysis was conducted for the myco-toxin standard mixture of AFB 1,AFB 2,AFG 1,AFG 2,OTA,DON,FB 1,FB 2,ZEA,T-2and HT-2toxins at the optimised LC-MS/MS conditions.Eight-point calibration curves were plotted as the peak area ratio (y )of each mycotoxin against its concentration (y =mx ±c )at the concentration ranges of 0.03–300μg kg −1for AFB 1and AFG 1;0.009–90μg kg −1for AFB 2and AFG 2;0.02–400μg kg −1for OTA;0.5–5000for DON,FB 1and FB 2;0.2–4000for ZEA;and 0.1–1000for T-2and HT-2.The linearity range was set slightly wider to include both high and trace levels due to the natural occurrence of the selected mycotoxins in contaminated PKC samples.Each datum point on the calibration curve was evaluated in triplicate and at the end the linearity was assessed by the correlation coef ficient (R 2).All the working solutions used for linearity test were filtered with a 0.22-µm filter and vortexed for 1min prior to the analysis.Limit of detection (LOD)and limit of quanti fication (LOQ)The LOD for a given analyte is the minimal amount needed to be able to distinguish the analyte signal above the background detector noise.The LOQ of an analyte is the lowest amount of the analyte in a sample that can be accurately measured with reliability.In this study the LODs and LOQs were calculated based on the less sensi-tive mass transition of standard and sample extracts by using the signal-to-noise (S /N )ratio of 3and 10for LOD and LOQ respectively.In order to check the variability of LOD and LOQ between mycotoxin standard and sampleFood Additives &Contaminants:Part A2073D o w n l o a d e d b y [U n i v e r s i t y o f J i a n g n a n ] a t 22:26 23 D e c e m b e r 2014matrix,the LODs and LOQs were assessed in both myco-toxin standard solution and PKC samples.Recovery and precisionThe recovery and precision of the LC-MS/MS method were assessed by spiking experiments at three different concentra-tion levels (low,median and high level)for each of the short-listed mycotoxins,as shown in Table 4.Prior to the extraction the spiked PKC samples were subsequently left overnight at RT in the dark to allow solvent evaporation and to establish equilibration between the analytes and the matrix.As no CRMs were commercially available,PKC samples that were found to contain only trace levels of mycotoxins were used as blank material for the spiking experiments.The recovery experiments for the whole analytical procedure were carried out in triplicate and the recovery values were obtained by calculation of the percentage of the measured amount of each mycotoxin to its spiked level.The precision was demonstrated as repeatability (intra-and inter-day repeatability).Intra-day repeatability was determined using 10replicate extractions of PKC on the same day.Inter-day repeatability test was performed by repeating the same procedure on three different days.Method veri ficationIn the final phase the newly developed LC-MS/MS method was successfully applied to the simultaneous quanti fication of AFB 1,AFB 2,AFG 1and AFG 2,OTA,ZEA,DON,FB 1and FB 2,T-2and HT-2toxin in 25PKC samples.Results and discussionLC-MS/MS method developmentDue to the mycotoxins ’wide range of polarity strength and relatively different physical and chemical properties,it is essential to determine optimal elution conditions for the simultaneous multi-mycotoxin analysis.In this study,the mobile phase composition with an appropriate gradient time frame,flow rate and injection volume was considered to be the key factor that greatly affected the chromato-graphic responses.Peak area was used for quanti fication.Hence,the same method has been used for the quanti fica-tion of mycotoxins in previous studies (Lattanzio et al.2007;Njobeh et al.2012).The best well-shaped chromatographic peaks of all mycotoxins with the highest peak areas and good sensitiv-ity were obtained with the mobile phase made of methanol (solution A)and 0.2%formic acid in water (solution B).The gradient elution programme began with 10%solution A and 90%solution B (0–8min),then changed to the gradient elution (8–10min)with 90%solution A and 10%solution B,followed by isocratic elution until 17min(10–17min).After the emergence of last peak,in order to clean more organic fraction the methanol percentage has to be deceased to the initial lowest concentration.With the consideration of the lag of time between the pump and the column,3min (17–20min)were allocated to change this isocratic elution to the linear decrease of methanol percen-tage from 90%to 10%.After that this composition was held until the end of the run (20–25min)to re-equilibrate the analytical column and prepare it for the next injection.Moreover,the flow rate of 200µl min −1with an injection volume of 25µl demonstrated better chromatograms of the mycotoxins with less noise than that at the other levels.The addition of formic acid to the mobile phase signi ficantly improved the peak shape and MS signals of FB 1and FB 2.The four carboxylic groups in fumonisins ’molecular struc-tures resulted in the usage of acidic elution conditions (Cavaliere et al.2005).Acetic acid has been used as a mobile phase additive with methanol or acetonitrile by some researchers (Herebian et al.2009;Lattanzio et al.2011;Soleimany et al.2011);formic acid with acetonitrile also has been reported (Zachariasova et al.2010).However,in this study,using acetic acid with methanol or acetonitrile and using formic acid with acetonitrile did not give as good chromatographic results,in terms of signal intensity and peak areas,compared with using methanol with formic acid.This difference may be explained by the higher acidity of formic acid,which can enhance fumonisins ’ionisation more than acetic acid.In addition,other researchers have used 0.1%formic acid with methanol (Tang et al.2012;Kong et al.2013).However,in this work,0.2%formic acid resulted in a better peak shape and higher signal inten-sity for fumonisins than 0.1%formic acid.Eventually,methanol with 0.2%formic acid in water was chosen as the best mobile phase composition.As a result,good separation of all 11mycotoxins was achieved with the lowest noise,indicating that these optimal elution conditions provided sensitive and ef ficient simultaneous determination of multi-mycotoxins in PKC.With regards to the MS/MS parameters,a satisfactory sensitivity for the target compounds was obtained by applying the ESI interface in both negative-ion mode for DON and in positive-ion mode for the other mycotoxins,as described by Soleimany et al.(2011).Consequently,the selected optimal MS parameters of the corresponding compounds in both positive-and negative-ion modes were chosen,and are summarised in Table 2.Figure 1shows the LC-MS/MS chromatogram of these mycotoxins in SRM under optimal elution conditions.Method validationEvaluation of the newly developed LC-MS/MS method performance was conducted for each of the 11target mycotoxins.A good linearity for this method was achieved with correlation coef ficients of a linear range of2074S.Yibadatihan et al .D o w n l o a d e d b y [U n i v e r s i t y o f J i a n g n a n ] a t 22:26 23 D e c e m b e r 20140.9863(for DON)and 0.9999(for T-2and HT-2),as given in Table 3.The intercepts on the linear equations appeared to be not close to zero.Analysis of the blank standards was performed and some signi ficant signals were found.The fact that this point was not close to zero could be related to the experimental conditions,baseline/back-ground and maybe other unknown reasons.The LODs and LOQs in standard solution and PKC matrices ranged from 0.02to 17.5μg kg −1and from 0.06to 58μg kg −1,respectively (Table 3).The results are acceptable because they are far below the European Union Regulations for reported maximum levels of mycotoxins in poultry feed.The LOD results are lower than those reported by Herebian et al.(2009)(0.5–90μg kg −1)and Ates et al.(2013)(1–150μg kg −1),while they are comparable with those reported by Soleimany,Jinap,Faridah,et al.(2012)(0.01–25μg kg −1)and de Lourdes Mendes de Souza et al.(2013)(0.4–20μg kg −1).Regarding the recoveries,satisfactory results were obtained within the range of 81–112%for all the 11mycotoxins,which are summarised in Table 4.The recov-eries were better than those reported by Ren et al.(2007)(76.2–102.0%)and de Lourdes Mendes de Souza et al.(2013)(51–107%),similar to those reported by Herebian et al.(2009)(71–112%),Zachariasova et al.(2010)(94–106%),Varga et al.(2012)(97–111%),Rodríguez-Carrasco et al.(2012)(60–116%)and Soleimany,Jinap,Faridah,et al.(2012)(83.5–107.3%)for the relevant mycotoxins.The intra-and inter-day precision valueswere in the range of 1.41–14.35%and 1.72–16.97%respectively.All the recovery and precision results were in agreement with performance criteria recommended by European Commission Regulation No.401/2006/EC (EC 401/2006).Method veri ficationThe quanti fication results for the application of the LC-MS/MS method to the 25PKC samples are summarised in Table 5.From the results it is clear that PKC is particularly prone to contamination with ZEA because all the samples were found to be positive for ZEA.The second most prevalent mycotoxin in PKC was AFG 2,which was found in 96%of the samples (24out of 25),followed by AFB 1and AFG 1,which were found in 92%of the samples (23out of 25).In contrast,the least prevalent mycotoxin for PKC was FB 1with the presence of 68%(17out of 25).The results illustrate that a total 60%of the samples (15out of 25)exceeded the maximum limits of 100and 400μg kg −1for total a flatoxins (AFB 1+AFB 2+AFG 1+AFG 2)and ZEA,respectively.Of these samples,one was contaminated with 435.20μg kg −1of ZEA and 14samples were con-taminated with total a flatoxins at levels of 214.48,225.85,114.67,208.72,213.02,106.68,172.06,124.39,101.25,206.44,217.68,116.31,123.11and 139.16μg kg −1.It is important to emphasise that the co-occurrence of mycotoxins in PKC is a common issue,as all the 25PKC samples were contaminated with at least seven of the 11Table 2.Mass spectrometry parameters for under optimised conditions.Analyte Precursor ion (m/z )Product ions (m/z )Collision energy (v)Tube lens Q1PW Q3PW AFB 1313.040[M +H]+24138940.70.7313.040[M +H]+28522940.70.7AFB 2315.060[M +H]+259291140.70.7315.060[M +H]+287261140.70.7AFG 1329.050[M +H]+243271310.70.7329.050[M +H]+28351310.70.7AFG 2331,070[M +H]+245221700.70.7331.070[M +H]+275211700.70.7OTA 404.000[M +H]+221231700.70.7404.000[M +H]+23961700.70.7ZEA 319.000[M +H]+185161700.70.7319.000[M +H]+18761700.70.7DON295.000[M –H]–24725900.70.7295.000[M –H]–26525900.70.7T-2489.000[M +H]+245261700.70.7489.000[M +H]+387221700.70.7HT-2447.000[M +H]+285351700.70.7447.000[M +H]+347191700.70.7FB 1722.050[M +H]+334411320.70.7722.050[M +H]+35235870.70.7FB 2706.040[M +H]+318371910.70.7706.040[M +H]+336351320.70.7Note:PW,peak width.Food Additives &Contaminants:Part A2075D o w n l o a d e d b y [U n i v e r s i t y o f J i a n g n a n ] a t 22:26 23 D e c e m b e r 2014RT:0.00 - 25.00SM:15GTime (min)50100050100050100050100050100RT:0.00 – 25.02SM:15G 024681012141618202224Time (min)05010005010005010005010005010005010013.6245.3225.5116.6918.5920.3621.3013.260.87 1.479.353.78 5.8410.588.316.8513.5515.2917.5320.3121.6419.385.2722.5824.791.811.1011.362.64 6.188.314.389.1513.3714.8021.6422.3517.4018.9612.692.671.8424.4611.054.547.2010.306.238.4213.2914.804.789.153.7915.277.022.8019.339.9917.252.0510.4024.4322.8219.9312.4210.1115.8114.508.1823.2817.2619.945.8920.9618.284.4818.758.1 3.730.8114.8012.4015.9418.2823.4649.3179.0 2.04 6.5522.763.06 5.698.2910.799.6720.523.94NL: 6.52E6TIC F: + c ESI SRM ms2 313.040 [240.995–241.005, 284.995–285.005] MS vial9-2NL: 1.12E5TIC F: + c ESI SRM ms2 315.060 [258.995–259.005, 286.995–287.005] MS vial9-2NL: 8.74E5TIC F: + c ESI SRM ms2 329.050 [242.995–243.005, 282.995–283.005] MS vial9-2NL: 2.13E4TIC F: + c ESI SRM ms2 331.070 [244.995–245.005, 274.995–275.005] MS vial9-2NL: 2.19E4TIC F: - c ESI SRM ms2 295.000 [246.995–247.005, 264.995–265.005] MS vial9-2NL: 2.55E5TIC F: + c ESI SRM ms2 319.000 [184.995–185.005, 186.995–187.005] MS vial9-2Figure 1.LC-MS/MS chromatogram of 11mycotoxins under optimised conditions at concentrations of 3μg kg −1for AFB 1and AFG 1,0.9μg kg −1for AFB 2and AFG 2,4μg kg −1for OTA,50μg kg −1for DON,T-2,HT-2,FB 1and FB 2,and 40μg kg −1for ZEA.Table 3.Linearity,limits of detection (LODs)and limits of quanti fication (LOQs)of the optimised LC-MS/MS method for simulta-neous determination of mycotoxins.Mycotoxins LOD in standard (μg kg −1)LOQ in standard (μg kg −1)LOD in PKC sample (μg kg −1)LOQ in PKC sample (μg kg −1)Linear range (μg kg −1)R 2Regression equation AFB 10.060.20.54 1.80.54–3000.9998y =353171x –317315AFB 20.020.060.160.50.162–900.9996y =24170x +15373AFG 10.060.20.54 1.80.54–3000.9993y =27886x +17159AFG 20.020.060.160.50.162–900.9977y =13133x +33144OTA 0.020.070.20.060.2–4000.9993y =18770x –23374DON 6.521103310–50000.9843y =4535x +454ZEA 0.310.932–40000.9994y =1032x +43400T-21 3.33103–10000.9999y =46431x –31897HT-22 6.7516.73–10000.9999y =7013x +14090FB 1 5.61817.55818–50000.9936y =135715x –15274FB 25.61817.55818–50000.9943y=129501x –163822076S.Yibadatihan et al .D o w n l o a d e d b y [U n i v e r s i t y o f J i a n g n a n ] a t 22:26 23 D e c e m b e r 2014mycotoxins.To the authors ’knowledge this is the first study dealing with the simultaneous detection of 11myco-toxins in PKC.This study suggests that more investiga-tions are needed in this commodity to evaluate mycotoxin contamination levels more ef ficiently and to accentuate monitoring mycological contamination of PKC.ConclusionsA feasible and reliable LC-MS/MS multi-mycotoxin method was developed for the simultaneous determination of AFB 1,AFB 2,AFG 1and AFG 2,OTA,ZEA,DON,FB 1and FB 2,T-2and HT-2toxin.This method was successfully employed to quantify the 11mycotoxins in PKC samples.Within almost 16min all the 11analytes were detected withhigh signal intensity and peak area.The method validation and veri fication results showed that the method provides a sensitive and rapid multi-mycotoxins determination analy-sis for PKC.Furthermore,it is important to emphasise that the high sensitivity of this method enables one to apply crude sample extracts that are obtained from a simple,one-step extraction procedure without further clean-up.Due to the advantages of cost,time and labour ef ficiency,this method would be highly desirable for routine analysis.FundingThe authors acknowledge the Ministry of Education Malaysia for financial support through the Long-term Research Grant Scheme (LRGS)[project number 10214].Table 4.Accuracy and precision for mycotoxin determination in optimal LC-MS/MS conditions for spiked PKC samples.Mycotoxins Spiking level (μg kg −1)Recovery (%)Intra-day precision (%)Inter-day precision (%)Mycotoxins Spiking level (μg kg −1)Recovery (%)Intra-day precision (%)Inter-day precision (%)AFB 11089 1.72 3.87ZEA 20092 5.43 1.41201038.911.56400112 4.49 2.4140957.52 5.718001088.45 2.25AFB 2399 4.23 2.02T-210087 2.387.31684 3.11 2.3200101 2.5512.7612106 2.898.9400110 3.45 5.31AFG 110110 5.18 5.57HT-21008016.977.2420108 3.56 3.02200979.1412.374092 1.697.7840010412.1211.62AFG 2310616.379.33FB 125010110.96 2.02610311.74 2.665008811.36 2.5112111 6.19 3.44250095 1.98 2.31OTA 20967.29 1.98FB 225086 3.89 1.6240909.81 6.8500817.85 1.1580109 3.3414.172500907.375.48DON250857.5910.7950082 5.314.352500909.296.37Table 5.Mycotoxin contamination in PKC samples (total of 25samples).Mycotoxins Range of contamination (μg kg −1)Number of positivesamplesPercentage of positive samples (%)Minimum Maximum AFB 1 1.7618.892392AFB 2 5.0159.642288AFG 1 1.3160.722392AFG 219.4778.382496OTA 0.42 5.122184DON 49107.631976ZEA 31.29435.2025100T-27.0760.672288HT-2 6.2733.942184FB 122.03110.521768FB 218.3581.241872Food Additives &Contaminants:Part A2077D o w n l o a d e d b y [U n i v e r s i t y o f J i a n g n a n ] a t 22:26 23 D e c e m b e r 2014。

高效液相色谱法同时测定L_苏糖酸钙和柠檬酸的含量

高效液相色谱法同时测定L_苏糖酸钙和柠檬酸的含量

快速、简便、准确的实验方法。

此方法已成功应用于静脉输注甘露醇开放血脑屏障对头孢三嗪透过血脑屏障影响的研究中。

参考文献:[1] 赵 侠,孙培红,周 颖,等.离子对反相高效液相色谱法测定人血清和尿液中的头孢曲松[J ].中国临床药理学杂志,2002,18(3):204.[2] 张 玉,王凯平,谭红艾,等.胆道手术病人中头孢曲松钠的药动学[J ].中国医院药学杂志,2001,21(9):5372539.[3] G aillard JL ,Abadie V ,Cheron G ,et al .Concentrations of ceftriax 2one in cerebrospinal fluid of children with meningitis receiving dexamethasone therapy[J ].A nti micro A gents Chemother ,1994,38(5):120921210.[4] Buke AC ,Cavusoglu C ,Karasulu E ,et al .Does dexamethasone af 2fect ceftriazone penetration into cerebrospinal fluid in adult bacte 2rial meningitis[J ].Int J A nti microb A gents ,2003,21:4522456.[5] 黄 英,梁茂植,余 勤,等.血浆头孢曲松HPLC 测定法及其在胸外术后患者的应用[J ].中国抗生素杂志,2000,25(2):109.[6] 葛庆华,吴卫泽,支晓瑾,等.头孢曲松(罗氏芬)在T 管胆汁中药动学研究[J ].中华肝胆外科杂志,2004,10(1):23225.(本文编辑:姜 黄)收稿日期:2005-04-20作者简介:高 革(1966-),男,河南新乡人,本科,实验师,研究方向:分析测试实验研究。

巧克力英语作文

巧克力英语作文

Chocolate,a delicacy cherished by many,is a versatile ingredient that can be found in a variety of forms,from sweet treats to rich beverages.Here are some aspects of chocolate that one might explore in an English essay:1.Historical Origins:Delve into the history of chocolate,tracing its roots to the ancient Mesoamerican civilizations who first cultivated cacao trees.Discuss how it was consumed as a bitter beverage by the Mayans and Aztecs and how it evolved into the sweet treat we know today.2.Cultural Significance:Explore the cultural significance of chocolate in different societies.For instance,how it became a symbol of luxury in Europe after its introduction by the Spanish and how it is associated with celebrations and gifts in modern times.3.Types of Chocolate:Describe the different types of chocolate,such as dark,milk,and white chocolate,and their varying compositions.Discuss the impact of the percentage of cocoa solids on the flavor and health benefits.4.Production Process:Elaborate on the process of chocolate production,from the harvesting of cacao pods to the fermentation,drying,roasting,and grinding of the beans, and finally the conching and tempering processes that give chocolate its smooth texture.5.Health Benefits:Discuss the potential health benefits of chocolate,particularly dark chocolate with high cocoa content,which is rich in antioxidants and has been linked to heart health and cognitive function.6.Chocolate in Cuisine:Highlight the use of chocolate in various culinary creations, from desserts like chocolate cake and brownies to savory dishes and even in molecular gastronomy.7.Ethical Considerations:Address the ethical issues surrounding chocolate production, such as fair trade and child labor,and how consumers can make informed choices to support ethical practices.8.Chocolate Art and Craftsmanship:Appreciate the artistry involved in chocolate making, from handcrafted truffles to intricate chocolate sculptures,and the skill of chocolatiers who create edible works of art.9.Global Impact:Examine the global impact of the chocolate industry,including its economic influence,environmental considerations,and the role of multinational corporations versus artisanal chocolate makers.10.Personal Experiences:Share personal experiences with chocolate,such as favorite childhood memories associated with chocolate treats,or a memorable visit to a chocolate factory or shop.When writing an essay on chocolate,its important to choose a specific angle or a combination of angles that interest you e descriptive language to engage the readers senses and provide a rich,nuanced exploration of the topic.。

一种测定污水中对苯二酚的新方法

一种测定污水中对苯二酚的新方法

一种测定污水中对苯二酚的新方法胡文娜【摘要】The copper and poly para aminobenzoic acid compoud modified electrode was prepared by the cy⁃clic voltammetry. And the electrochemical behavior of hydroquinone on the modified electrode was studied. In pH3.5 phosphate buffer solution,with the scanning rate of 240 mV/s,hydroquinone produced a clear pair of redox peaks,and the peak potential were Epa= 0.376 V and Epc = 0.293 V,respectively. Hydroquinone oxi⁃dation peak current and concentration in the range of 3.0 × 10-6~1.0 × 10-3 mol/L had a good linear relation⁃ship,and the detection limit was 8.0×10-7 mol/L. Based on the study,a new method was established forde⁃termination of hydroquinone.And the method was used for the determination of hydroquinone samples with satisfactory results.%用循环伏安法制备铜/聚对氨基苯甲酸复合修饰电极,并研究对苯二酚在该修饰电极上的电化学行为.在pH3.5磷酸盐缓冲溶液中,扫描速率为240 mV/s时,对苯二酚会在铜掺杂修饰电极上产生一对清晰的氧化还原峰,峰电位分别为Epa=0.376 V,Epa=0.293 V.对苯二酚氧化峰电流与其浓度在3.0×10-6~1.0×10-3 mol/L范围内呈良好的线性关系,检出限为8.0×10-7 mol/L.基于对苯二酚在修饰电极上的电化学特性,为我们建立一种新的测定方法.对对苯二酚样品的测定分析,结果满意.【期刊名称】《淮北师范大学学报(自然科学版)》【年(卷),期】2015(000)003【总页数】4页(P49-52)【关键词】铜;对氨基苯甲酸;对苯二酚;循环伏安法;修饰电极【作者】胡文娜【作者单位】蚌埠学院应用化学与环境工程系,安徽蚌埠 233030【正文语种】中文【中图分类】O657.15对苯二酚是一种白色针状结晶的有机化合物,广泛应用于生产染料,光稳定剂,感光材料等.但它是有毒有机物,污染环境,并难以降解[1].目前测定对苯二酚的方法主要有荧光法[2]、色谱法[3]和电化学法[4],这些方法中有的预处理比较麻烦,有的灵敏度较低.而氨基酸由于分子中含有氨基和羟基这两种官能团使得它具有许多独特的性质,人们可以利用电化学或化学方法将氨基酸固定到电极表面,能够广泛用于各种物质的分析[5-10],在测定生物分子,有机污染物、离子等方面显示出它的优越性,但有的氨基酸修饰电极的灵敏度还有待提高.将金属掺杂在基底修饰膜中,能够提升物质在电极上的电子传递速率[7,11-12].本文吸取二者的优点,采用循环伏安法,将金属铜与对氨基苯甲酸掺杂共聚到玻碳电极表面,制得铜/聚对氨基苯甲酸复合修饰电极,并研究对苯二酚在修饰电极上的电化学特性.通过制备条件和测定条件的优化,使得该修饰电极能够很好地用于对苯二酚的测定.结果表明,铜/聚对氨基苯甲酸复合修饰电极制备简单,测定污水样品中对苯二酚结果满意.1 实验部分1.1 实验仪器与试剂CHI660E电化学分析系统(上海辰华有限公司),pHS-3C型酸度计,工作电极:玻碳电极(GCE)或铜/聚对氨基苯甲酸复合修饰电极(Cu-PPABA/GCE),对电极:铂丝电极,参比电极:Ag/AgCl电极.对苯二酚:0.010 mol/L,避光保存,使用时再逐级稀释;对氨基苯甲酸:0.010 mol/L,硝酸铜:0.010 mol/L,硝酸钾1.0 mol/L,磷酸盐缓冲溶液,均采用0.10 mol/L H3PO4,NaH2PO4,Na2HPO4,Na3PO4溶液配制,并在pH计上校准.实验所采用的试剂均为分析纯,所采用的水均为石英亚沸水.1.2 铜/聚对氨基苯甲酸复合修饰电极的制备将玻碳电极按文献[11]进行预处理,放入含有3.0×10-3 mol/L对氨基苯甲酸,8.0×10-3 mol/L硝酸铜,1.0×10-2 mol/L 硝酸钾,8.0×10-2 mol/L 硝酸的适量溶液中,在-0.8~2.2 V电位范围内,静止12 s,采用三电极系统,以100mV/s循环扫描16周.取出电极,用亚沸水洗涤,用滤纸吸干即可制得.1.3 实验方法在50 mL 容量瓶中加入适量的对苯二酚,然后用pH 3.5 的PBS 稀释至刻度,转入电解池,以Cu-PPABA/GCE 为工作电极,铂丝为对电极,Ag/AgCl 为参比电极,静置4 s 后以240 mV/s 的速率扫描,记录-0.1~0.9 V电位范围内的循环伏安曲线.每进行下一次测定之前都需要进行空白测定,使实验更加可靠与准确.2 结果与讨论2.1 Cu-PPABA/GCE修饰电极制备条件的选择2.1.1 对氨基苯甲酸和硝酸铜浓度的影响作为修饰底液的主要成分,对氨基苯甲酸会影响到修饰膜的形态及稳定性,硝酸铜的浓度则会影响到修饰膜中铜的含量.铜含量过低,电子传递速率提升不明显,硝酸铜的浓度过大,铜峰增大,在测定电位窗口中会影响对苯二酚的测定.实验发现随着对氨基苯甲酸浓度和Cu(NO3)2浓度的升高,Cu-PPABA/GCE 电极对对苯二酚的响应先增大后减小,综合考虑测定的灵敏度和峰型,选定Cu(NO3)2浓度8.0×10-3 moL/L,对氨基苯甲酸浓度3.0×10-3 moL/L进行实验.2.1.2 聚合底液pH及硝酸钾的影响硝酸和硝酸钾在聚合液中起到的作用是不同的.前者主要控制底液的酸度,进而影响修饰膜中氨基酸的荷电情况,后者则是起到支持电解质的作用.改变硝酸和硝酸铜的浓度进行实验,结果发现,随着酸度和支持电解质含量的增加,对苯二酚在该修饰电极上的响应电流均呈现先增大后减小的现象.故选定当硝酸浓度8.0×10-2 mol/L时,硝酸钾浓度1.0×10-2 mol/L进行聚合.2.1.3 聚合周期的影响采用已优化的底液浓度,改变聚合周期进行实验,改变扫描次数.实验表明,当聚合周次较少时修饰电极对对苯二酚的响应电流小,16周时响应电流达到最大值后逐渐降低.这是由于扫描周期少,则导致电极上聚合物含量低,活性的基团较少,从而使得修饰电极对于对苯二酚测定的灵敏度低;扫描周期过多,会造成聚合薄膜过厚,使得反应的电子传递在聚合薄膜中的阻力过大,最终导致响应电流减小.因此选定扫描次数为16周.2.1.4 聚合扫描速度的影响改变聚合扫描速率从20~300 mV/s,每隔20 mV/s依次进行实验.聚合扫描速率对于测定分析的精密度有较大影响.聚合物在电极表面沉积过快,会使得聚合膜的表面过于粗糙且形态不规整,聚合物沉积太慢,虽会使聚合膜相对致密,但耗费时间过长.因此选定扫描速度为100 mV/s.2.1.5 铜/聚对氨基苯甲酸复合修饰电极的聚合循环伏安曲线图1为铜掺杂聚对氨基苯甲酸在最佳条件下的循环伏安图.从图1中可以看出第一圈在0.20 V左右出现一明显的氧化峰,这可能是沉积的金属铜溶出形成的.该峰在第二圈开始,峰电位逐渐移至0.10 V,峰电流迅速减弱并趋于稳定,这说明铜的沉积趋于平衡,聚合膜逐渐完整,使得铜被共聚电极表面.同时可能由于对氨基苯甲酸氧化聚合的原因导致在0.80 V左右出现一个较宽的氧化峰.图1 Cu-PPABA/GCE的CV曲线图2 对苯二酚在裸电极(1)和Cu-PPABA/GCE(2)上的循环伏安曲线2.2 对苯二酚测定条件的优化2.2.1 对苯二酚在修饰电极上的循环伏安特性将5.0×10-4 mol/L的对苯二酚取适量于pH 3.5的磷酸盐缓冲溶液中进行测定.由图2可看出,对苯二酚在裸电极上测定时没有明显响应,而在Cu-PPABA/GCE 有一对明显的氧化还原峰,峰电位分别为Epa=0.376 V和Epa=0.293 V,且峰电流较大.从而可以说铜与聚对氨基苯甲酸修饰电极后,Cu-PPABA/GCE对对苯二酚有很强的电催化作用且也有很好的灵敏度.2.2.2 pH对对苯二酚的电化学行为影响在优化的聚合条件下制备出Cu-PPABA/GCE,采用循环伏安法在pH 2.5-11.0之间对1.0×10-4 mol/L对苯二酚进行实验(如图3).从实验结果可以发现,随着pH的增加,对苯二酚的峰电位均负移,且峰电位与pH 的线性方程为:Epa(V)=0.565 6-0.052 41 pH,R=0.999 2;Epc(V)=0.532 1-0.055 32 pH,R=0.993 6,说明对苯二酚在该修饰电极上反应有质子参加,且是等电子等质子反应.pH 2.5~8.0之间,对苯二酚的氧化和还原峰电流均先增大后减小,pH 3.5时达到最大;pH>8.0后,峰电流迅速减小并逐渐消失.此时,对苯二酚溶液也开始变红,这可能是碱性条件下,对苯二酚转化成酚钠,更容易被空气氧化所致.故选定最佳pH为3.5.图3 不同pH时对苯二酚在铜/聚对氨基苯甲酸复合修饰电极上的CV曲线图4 不同扫速时对苯二酚在铜/聚对氨基苯甲酸复合修饰电极上的CV曲线2.2.3 扫速对对苯二酚电化学行为的影响在pH 2.5的磷酸盐缓冲溶液中,改变扫速来对5.0×10-4mol/L对苯二酚进行测定(如图4).从实验数据中可以看出,随着扫描速率的增加,对苯二酚的峰电流逐渐增大,在20~500 mV/s之间,Ipa=0.448 8 υ1/2+0.824 8,R=0.991 1,说明对苯二酚的氧化过程主要受扩散控制.同时,随着扫速的增加,峰电位差逐渐增大,充电电流逐渐增加,峰型变差,反应的可逆性降低.综合考虑测定灵敏度和反应可逆性,选择240 mV/s时为最佳测定扫速.2.2.4 工作曲线、稳定性和干扰物质测定在优化的聚合条件和测定条件下进行实验.在3.0×10-6~1.0×10-3mol/L 之间,对苯二酚的氧化峰电流与其浓度呈线性关系,回归方程为Ip(aμA)=60.450 C+17.195,R2=0.992 9,检出限为8.0×10-7mol/L.对3.0×10-4mol/L对苯二酚平行测定30次,RSD为4.0%.该修饰电极在室温下放置10 d,对苯二酚响应电流及电位基本不变,说明该修饰电极具有较好的稳定性.允许误差在±5%,在3.0×10-4mol/L对苯二酚中,试验一些常见的离子.结果显示,Fe3+、Cd2+,Sr2+,Cr3+,Al3+,Zn2+,Bi3+,Pb2+,抗坏血酸均不形成干扰(0.5 mg,未作最高限).2.2.5 样品分析取一定量对苯二酚稀释至一定浓度按实验方法采用标准加入法进行回收率的测定,结果见表1.表1 样品分析结果样品对苯二酚加入量(×10-4 mol/L)5.00 8.00测定值(×10-4 mol/L)4.92 7.67回收率/%98.4 95.83 结论本实验通过循环伏安法将铜和对氨基苯甲酸修饰共聚在玻碳电极上,成功地制备了铜/聚对氨基苯甲酸复合修饰电极.并对对苯二酚在修饰电极上的电化学特性进行了研究,得到铜/聚对氨基苯甲酸复合修饰电极测定对苯二酚时的最佳条件,建立测定对苯二酚的新方法,并且测定时稳定安全可靠,选择性高,灵敏度好.参考文献:[1]ZHAO D M,ZHANG X H,FENG L J,et al.Simultaneous determination of hydroquinone and catechol at PASA/MWNTs composite film modified glassy carbon electrode[J].Colloids and Surf B,2009,74(1):317-321.[2]李淮芬,谢成根,宗佳佳,等.同步荧光法同时测定苯二酚中邻苯二酚和对苯二酚[J].冶金分析,2009,29(9):31-35.[3]黄少鹏,徐金瑞,王琼.薄层色谱法同时测定邻苯二酚、间苯二酚和对苯二酚异构体[J].分析化学,1999,27(3):331-333.[4]YU J J,DU W,ZHAO F Q,et al.High sensitive simultaneous determination of catechol and hydroquinoneat mesoporous carbon CMK-3 electrode in comparison with multi-walledcarbon nanotubes and vulcan XC-72 carbon electrodes[J].Bio⁃electronchem,2012,135(2):446-451.[5]王广凤,李茂国,方宾,等.巯基二茂铁衍生物的合成及其生物传感器的制备与应用[J].应用化学,2005,22(2):168-170.[6]MATSUNAGA M,NAKANISHI T,ASAHI T,et al.Effect of surface coverage of gold(111)electrode with cysteine on the chiral discrimination of DOPA[J].Chirality,2007,19(4):295-299.[7]孙登明,马伟.银掺杂聚L-天冬氨酸修饰电极的制备及对多巴胺的测定[J].应用化学,2008,25(8):913-915.[8]YEH W L,KUO Y R,CHENG S H.Voltammetry and flow-injection amperometry for indirect determination of dopamine[J].Electrochemistry Communications,2008,10(1):66-70.[9]LI Y X,HUANG X,CHEN Y L,et al.Simultaneous determination of dopamine and serotonin by use of covalent modifica⁃tion of 5-hydroxytryptophan on glassy carbon electrode[J].Microchim Acta,2009,164(1):107-112.[10]赵艳霞,马心英,王琦.聚L-赖氨酸修饰电极对去甲肾上腺素的电催化氧化[J].分析试验室,2005,24(3):71-74.[11]HU W N,SUN D M,MA W.Silver doped poly(L-valine)modified glassy carbon electrode for the simultaneous determi⁃nation of uric acid,ascorbic acid and dopamine[J].Electroanalysis,2010,22(5):584-589.[12]杨欣,王峰,刘璐,等.纳米金掺杂石墨烯修饰玻碳电极选择性测定多巴胺[J].食品工业科技,2012,33(8):88-91.。

离子色谱法同时测定饮用水中一碘乙酸、二碘乙酸

离子色谱法同时测定饮用水中一碘乙酸、二碘乙酸

化学分析计量CHEMICAL ANALYSIS AND METERAGE第29卷,第4期2020年7月V ol. 29,No. 4Jul. 202062doi :10.3969/j.issn.1008–6145.2020.04.014离子色谱法同时测定饮用水中一碘乙酸、二碘乙酸王存进1,代文彬1,钟志雄2(1.青岛睿谱分析仪器有限公司,青岛 266000; 2.广东省疾病预防控制中心,广州 510000)摘要 建立离子色谱法同时测定饮用水中一碘乙酸和二碘乙酸的方法。

样品经Na 柱、RP 柱和滤膜过滤后直接进样分析,采用Ionpac AS19(4.0 mm ×250 mm ,7.5 μm )色谱柱,氢氧化钾梯度淋洗,抑制电导检测进行测定。

一碘乙酸、二碘乙酸的质量浓度在0.002~0.1 mg /L 范围内与色谱峰面积线性关系良好,相关系数不小于0.999 0。

采用氢氧根淋洗液和动态量程电导检测器可以获得nS 级的噪声,检出限达到ng /L 级。

自来水和黄河水中均未检出一碘乙酸、二碘乙酸,加标回收率在85.25%~115.00%,测定结果的相对标准偏差为0.49%~3.77%(n =6)。

该方法精确度高,回收率和重现性良好,是检测新型碘代酸消毒副产物的可靠方法。

关键词 一碘乙酸;二碘乙酸;离子色谱法;氢氧根梯度淋洗中图分类号:O657.7 文献标识码:A 文章编号:1008–6145(2020)04–0062–05Simultaneous determination of monoiodoacetic acid and diiodoacetic acid in drinking waterby ion chromatographyWANG Cunjin 1,DAI Wenbin 1,ZHONG Zhixiong 2(1. Qingdao Reepo Analytical Instrument Co.,Ltd.,Qingdao 266000,China;2. Guangdong province center for disease control and prevention ,Guangzhou 510000,China )Abstract A method was developed for the simultaneous determination of monoiodoacetic acid and diiodoacetic acid in drinking water by ion chromatography. Sample was treated by Na column, RP Column and filtration for direct injection.The method use of Ionpac AS19 (4.0 mm ×250 mm, 7.5 μm) column and KOH gradient elution for separation and suppressed conductivity for detection. The mass concentration of monoiodoacetic acid and diiodoacetic acid showed good linear relationship with the peak area in the range of 0.002–0.1 mg /L, and the correlation coef ficient were not less than 0.999 0. The detection limits were down to ng /L due to the use of hydroxide eluent and dynamic range conductivity detector with nS baseline noise. There was no monoiodoacetic acid or diiodoacetic acid in tap water and Yellow River water, the stangard addition recovery was 85.25%–115.00%, and the relative standard deviations of determination results were 0.49%–3.77%, respectively. The method has high accuracy, good recovery and reproducibility, and is a reliable method for the detection of new iodoacid disinfection by–products.Keywords monoiodoacetic acid; diiodoacetic acid; ion chromatography; hydroxide gradient elution随着城市化水平的不断提高和城市集中供水方式的发展,生活饮用水的水质问题逐渐引起人们的注意。

石墨烯修饰电极同时测定邻苯二酚和对苯二酚

石墨烯修饰电极同时测定邻苯二酚和对苯二酚

石墨烯修饰电极同时测定邻苯二酚和对苯二酚万其进;廖华玲;刘义;魏薇;舒好;杨年俊【摘要】制备石墨烯玻碳修饰电极,进而采用循环伏安法、交流阻抗等电化学方法对该电极进行表征,研究该石墨烯修饰电极在邻苯二酚和对苯二酚上的电化学行为.结果表明,在石墨烯修饰电极上邻苯二酚的氧化峰电位和还原峰电位分别是270 mV和161 mV,对苯二酚氧化峰电位和还原峰电位分别是145mV和64 mV,由于邻苯二酚和对苯二酚的氧化峰电位大约相离125 mV,还原峰大约相离97 mV,因此适合同时检测邻苯二酚和对苯二酚.邻苯二酚和对苯二酚的浓度在5.0×10-6~1.0×10-4 mol/L范围内与峰电流分别呈良好的线性关系;且在8.0×10-5~1.0×10-3 mol/L范围能同时检测邻苯二酚和对苯二酚,邻苯二酚的检测限可达5.0×10-7 mol/L,对苯二酚的检测限可达1.0×10-7 mol/L.该石墨烯修饰电极可作为电化学传感器用于邻苯二酚和对苯二酚的含量同时测定及环境水体中实际样品的分析.%A novel graphene modified glassy carbon electrode was fabricated. The resulting substrates were characterized by Cyclic Voltammetry and EIS in [Fe (CN)6 ]3-/4- solution and showed the electrochemical behavior of catechol and hydroquinone on the graphene modified glassy carbon electrode. Experiment result shows that the catechol oxidation peak potential is 270 mV and reduction peak potential is 161 mV, and the hydroquinone oxidation peak potential is 145 mV and reduction peak potential is 64 mV on the graphene modified electrode, respectively. The oxidation peak potential distance is about 125 mV and the reduction peak potential distance is about 97 mV of catechol and hydroquinone which are suited for the simultaneous detection. Catechol and hydroquinone havegood electrocatalytic activity on modified electrode and the peak currents of differential pulse voltammetry are liner to the catechol and hydroquinone over the range of 5. 0× 10-6 —1. 0× 10~4 mol/L, respectively, and the graphene modified electrode can simultaneously detect catechol and hydr oquinone in the rang of 8. 0× 10-5 —1. 0 × 10-3 mol/L. The catechol detection limit is 5. 0 × 10-7 mol/L, the hydroquinone detection limit is 1. 0 × 10-7 mol/L. So the graphene modified electrode can be used for analysis the facilitation of actual samples and electrochemical sensors and biosensors.【期刊名称】《武汉工程大学学报》【年(卷),期】2013(035)002【总页数】8页(P16-23)【关键词】石墨烯;修饰电极;示差脉冲法;邻苯二酚;对苯二酚【作者】万其进;廖华玲;刘义;魏薇;舒好;杨年俊【作者单位】武汉工程大学绿色化工过程教育部重点实验室,湖北省新型反应器与绿色化学工艺重点实验室,湖北武汉430074【正文语种】中文【中图分类】O657.10 引言石墨烯(Graphene),又称单层石墨,是一种由碳原子以sp2杂化轨道组成六角型呈蜂巢晶格的平面薄膜,只有一个碳原子厚度的二维材料[1].石墨烯是世上最薄却也是最坚硬的纳米材料[2],导热系数高达5 300 W/(m·K)[3],高于碳纳米管和金刚石,常温下其电子迁移率超过15 000 cm2/(V·s),又比纳米碳管或硅晶体高,而电阻率只约10-6Ω·cm,比铜或银更低,为目前世上电阻率最小的材料,其敏锐的导电性能用于电材料时有利于促进电子的转移,提供了一种新型的方式于电化学传感器和生物传感器[4-11].因为它的电阻率极低,电子跑的速度极快,因此提供了一种新的方式来研究电化学和生物传感器.已有报道石墨烯成功的应用于研究和检测一些生物和有机分子,包括 DNA[4-5],葡萄糖[6-7],NADH[5],过氧化氢[5],多巴胺[5,8-11],抗坏血酸[5,8-11],尿酸[5,8-11],血清素[9]等.邻苯二酚和对苯二酚是酚的两种同分异构体,是医药、食品和环境中的重要污染物.因此,建立一种快速、灵敏、简单、准确的测定邻苯二酚和对苯二酚的方法非常有意义.已经报道的邻苯二酚和对苯二酚的检测方法有气相色谱(GC)分析方法、荧光光度法、吸光度比值导数法、紫外分光光度法及双波长比值法等[12-16],但这些方法大都仪器昂贵,灵敏度低,且前处理复杂.相比于上述方法,电化学方法[17]具有仪器简单、选择性好、灵敏度高等优点.用石墨烯修饰电极检测塑料和水样中的邻苯二酚和对苯二酚已有报道[17-18].本实验将3 mg石墨烯分散于1 m L DMF中超声分散30 min,取适量分散液滴涂于已经处理好的玻碳电极表面,红外烘干,即制得石墨烯修饰电极(GR/GCE),用循环伏安法[19]研究了 CC和HQ在磷酸氢二钠-柠檬酸缓冲溶液中的电化学行为[20],并对一系列浓度的CC和HQ进行了电化学测定,得到了较好的实验结果.该石墨烯修饰电极有望用于实际污水中邻苯二酚和对苯二酚含量的测定.1 实验部分1.1 仪器与试剂CHI760B电化学工作站(上海辰华仪器公司),KQ-250型超声波清洗器(昆山市超声仪器有限公司),三电极系统:玻碳电极或修饰电极为工作电极;饱和甘汞电极为参比电极;铂丝电极为对电极.石墨烯(Graphene Nanopowder 8 nm flakes);邻苯二酚和对苯二酚(上海三浦化工有限公司);磷酸氢二钠-柠檬酸溶液作为支持电解质;K 3 Fe(CN)6 溶液:0.02 mol/L;避光保存.其它试剂均为分析纯,实验用水均为超纯水;实验均是在室温下进行.1.2 石墨烯修饰电极的制备将3 mg石墨烯超声分散于1 m L DMF中,得到石墨烯悬浊液,然后用微量进样器取适量石墨烯分散液滴涂在预处理好的玻碳电极表面,红外烘干,即得到石墨烯修饰电极.2 结果与讨论2.1 GR/GCE循环伏安特性根据 Hrapovic和 Yang 的观点[21-22],纳米材料电活性表面积越大,电催化性能越好,灵敏度越高.因此,选择循环伏安法来计算修饰电极电活性表面积.图1为裸电极(a)和 GR/GCE(b)分别在5×10-3 mol/L[Fe(CN)6]3-/4溶液中的循环伏安图,可以看出与裸电极相比,GR/GCE的峰电流明显增加,这表明石墨烯修饰电极拥有较大的电活性表面积.图1 裸电极(a)和石墨烯修饰电极(b)在5×10-3 mol/L[Fe(CN)6]3-/4溶液中的循环伏安图Fig.1 CV of bare glassy carbon electrode(a)and GR/GCE(b)in 5×10-3 mol/L[Fe(CN)6■3-/4 at scan rate of 100 mv/s活性表面积可通过Randles-Sevcik方程I p=2.69×105 AD 1/2 n3/2 v1/2 c来计算.其中n代表参加氧化还原反应反应电子数,A表示电极的活性表面积(cm2),D 表示分子在溶液中的扩散系数(cm2/s),c为溶液浓度(mol/cm3),v 表示电位扫描速度(v/s).[Fe(CN)6]3-/4氧化还原体系是电化学研究最广泛的氧化还原对之一,属于单电子转移(n=1).当溶度为5×10-3 mol/L时,扩散系数(D)约为(6.79±0.02)×10-6 cm2/s.根据上述方程,可以计算出GR/GCE和裸电极的活性表面积的平均值分别为0.17cm2 和0.11 cm2,GR/GCE的活性表面积增加了54.5%.活性表面积的增加表明GR/GCE具有更好的电催化活性,适合作为电化学传感器和生物传感器.2.2 GR/GCE的交流阻抗特性用交流阻抗法分别对裸电极和GR/GCE进行了表征.如图2所示,在选定的频率范围内,裸玻碳电极(曲线a)上探针[Fe(CN)6]3-/4-的阻抗谱图在高频部分出现半圆,在低频部分得到近似直线,这说明裸玻碳电极表面对电子的传递存在一定的阻抗,而在GR/GCE(曲线b)上,探针[Fe(CN)6]3-/4-的阻抗谱图基本上是一条直线,表明此时电极上不存在阻碍电子传递的物质,[Fe (CN)6]3-/4-非常容易达到表面发生氧化还原反应.说明石墨烯修饰层起到了增强电子传输的作用,与裸电极相比,GR/GCE的电导性明显增强.图2 裸电极(a)和石墨烯修饰电极(b)的交流阻抗图Fig.2 Impedance plots of bare glassy carbon electrode(a)and GR/GCE(b)2.3 邻苯二酚和对苯二酚分别在不同电极上的电化学行为图3为5×10-4 mol/L的邻苯二酚(CC)分别在裸电极(a)和GR/GCE(b)上的循环伏安图.由此可见,邻苯二酚在裸电极上的电化学行为是不可逆的且响应相对较弱,其氧化峰电位是486 mV,而在GR/GCE上的电化学行为是准可逆的且响应相对较强,其氧化峰电位是270 mV,氧化峰电位负移了216 mV,峰电流显著增大达到276 mA.由此可见,GR/GCE对邻苯二酚产生了明显的电催化作用.图4为5×10-4 mol/L的对苯二酚(HQ)分别在裸电极(a)和GR/GCE(b)上的循环伏安图.由此可见,对苯二酚在裸电极上氧化过电位较高(大于600 m V),而在GR/GCE上的电化学行为是准可逆的且响应相对较强,其氧化峰电位是145 m V,氧化峰电流显著增大达到257 mA.由此可见,GR/GCE对对苯二酚产生了明显的电催化作用.图3 为5×10-4 mol/L CC在裸电极(a)和GR/GCE修饰电极(b)上的循环伏安图Fig.3 Cyclic voltammograms of bare electrode(a)and GR/GCE (b)in 5×10-4 mol/L CC图4 为5×10-4 mol/L HQ在裸电极(a)和GR/GCE修饰电极(b)上的循环伏安图Fig.4 Cyclic voltammograms of bare electrode(a)and GR/GCE (b)in 5×10-4 mol/L HQ2.4 最佳条件的选择2.4.1 支持电解质及p H的选择实验比较了邻苯二酚和对苯二酚在相同p H值的不同缓冲溶液如醋酸缓冲溶液、磷酸缓冲溶液、硫酸缓冲溶液、KH 2 PO4-NaOH 缓冲溶液、Na2 HPO4-柠檬酸缓冲溶液中的电化学行为,发现邻苯二酚和对苯二酚都在Na2 HPO4-柠檬酸缓冲溶液中表现出良好的电化学行为,二者的氧化还原峰较好,峰电流较高.配制p H5.4~6.0范围的 Na2 HPO4-柠檬酸缓冲溶液,研究了邻苯二酚和对苯二酚在GR/GCE上的电化学行为随p H值的变化情况.由图5可知,邻苯二酚在Na2 HPO4-柠檬酸缓冲溶液中峰电位和峰电流随pH的变化并不明显,随pH的增大峰电位稍有负移且峰电流略有下降,因此本实验对邻苯二酚的测定底液pH值选择为5.6,由图6可知,对苯二酚在Na2 HPO4-柠檬酸缓冲溶液中峰电位和峰电流随pH的变化明显,随pH的增大峰电流先增大后减小,在pH=5.8时峰电流达到最大,故本实验对对苯二酚的测定底液pH值为选择5.8.图5 pH对邻苯二酚在GR/GCE上的循环伏安图影响Fig.5 Cyclic voltammograms of GR/GCE in CC solution with different p H注:a pH=5.4,b pH=5.6,c pH=5.8,d pH=6.0,扫描速度:100 m V/s.图6 pH对对苯二酚在GR/GCE上的循环伏安图影响Fig.6 Cyclic voltammograms of GR/GCE in HQ solution with different pH注:a p H=5.4,b p H=5.6,c p H=5.8,d p H=6.0,扫描速度:100 m V/s.2.4.2 滴涂量的选择a.石墨烯浓度的选择在同一条件下分别滴涂1 mg/m L、3 mg/m L和5 mg/m L的石墨烯溶液在GCE电极上,测对苯二酚和邻苯二酚的响应,结果发现用3 mg/mL的石墨烯效果明显好一些.b.石墨烯滴涂次数的选择在其它实验条件不变的情况下,在裸电极表面分别滴涂不同量的石墨烯悬浊液,当悬浊液的滴涂量由4~18μL(3 mg/m L)变化时,氧化峰电流先增大后几乎不变最后略有减小,这可能是由于石墨烯厚度增加到一定程度而阻碍了电子的传递,故导致导电性变差.为了得到最佳峰电流和峰电位,邻苯二酚(图7)选择滴涂16μL,对苯二酚(图8)选择滴涂12μL.图7 邻苯二酚的峰电流与石墨烯滴涂量的关系Fig.7 The relationship between the peak current of CC and dispensing the quantity of graphene注:石墨烯滴涂量分别为4,6,8,10,12,14,16,18μL.图8 对苯二酚的峰电流与石墨烯滴涂量的关系Fig.8 The relationship between the peak current of HQ and dispensing the quantity of graphene注:石墨烯滴涂量分别为4,6,8,10,12,14,16,18μL.2.4.3 扫速的影响在其它条件不变的情况下,以不同的扫描速度分别对含邻苯二酚和对苯二酚的溶液进行CV扫描,如图9和10所示.从图中可知,随扫描速度的增加,二者的氧化还原峰电流明显增大.邻苯二酚(图9)在20~160 m V/s扫速范围内氧化还原峰电流与扫速的平方根呈良好的线性关系,线性回归方程为I Pa=-0.209 03+2.135E-4c,线性相关系数R=0.998 6表明石墨烯修饰电极/溶液界面上的电极反应为受扩散控制的电极过程,同样对苯二酚(图10)在20~160 m V/s扫速范围内氧化还原峰电流与扫速呈良好的线性关系,线性回归方程为I Pa=0.637 78+1.222E-5c,相关系数R=0.996 2,表明石墨烯修饰电极/溶液界面上的电极反应为受吸附控制的表面电极过程.图9 GR/GCE在5.0×10-4 mol/L邻苯二酚溶液中不同扫描速度的循环伏安图(A)和峰电流与扫描速度的关系(B)Fig.9 Cyclic voltammograms of the GR/GCE in 5.0×10-4 mol/L CC(A)and the relation between the peak currentsand different speed(B)注:扫速分别为20(a),40(b),60(c),80(d),100(e),120(f),140(g),160(h)m V/s.图10 GR/GCE在5.0×10-4 mol/L对苯二酚溶液中不同扫描速度的循环伏安图(A)和峰电流与扫描速度的关系(B)Fig.10 Cyclic voltammograms of the GR/GCE in 5.0×10-4 mol/L HQ(A)and the relation between the peak currentsand different speed(B)注:扫速分别为20(a),40(b),60(c),80(d),100(e),120(f),140(g),160(h)m V/s.2.4.4 富集时间和富集电位的影响由于对苯二酚在电极上的反应主要受吸附过程控制,所以每次测定前需要在选定电位条件下富集一段时间以达到良好的测定效果.研究不同富集时间对峰电流的影响(图11),随着富集时间的增大,峰电流先增大后减小,最佳富集时间为20 s.研究不同富集电位对电流的影响(图12),随着富集电位的减小,峰电流先增大后减小,最佳富集电位为-1.0 V.图11 对苯二酚富集时间与峰电流的关系Fig.11 The relationship between the peak current of HQ and deposit time图12 对苯二酚富集电位与峰电流的关系Fig.12 The relationship between thepeak current of HQ and deposit electrodes2.4.5 线性范围和检出限图13为在p H=5.6的磷酸氢二钠-柠檬酸缓冲溶液为底夜的条件下,石墨烯修饰电极在不同浓度的邻苯二酚溶液中的示差脉冲伏安(DPV)图.图14为在p H=5.8的磷酸氢二钠-柠檬酸缓冲溶液为底夜的条件下,石墨烯修饰电极在不同溶度的对苯二酚溶液中的示差脉冲吸附溶出伏安(DPADV)图.在5.0×10-6~1.0×10-4 mol/L溶度范围内,邻苯二酚和对苯二酚的氧化峰与其浓度有良好的线性关系.对应的线性回归方程:邻苯二酚是I pa=1.163 21 E-6+0.029 44c;相关系数R=0.998 2;检测限可达5.0×10-7 mol/L;对苯二酚是I pa=2.264 17E-6+0.335 82c;相关系数R=0.997 7;检测限可达1.0×10-7 mol/L.图13 不同浓度的邻苯二酚在GR/GCE上的DPV图(A)和峰电流和邻苯二酚浓度的关系(B)Fig.13 DPV for different concentrations of CC at the GR/GCE(A)and the relationship between the peak currents and concentrations(B)注:浓度分别为(a)4.0×10-6,(b)8.0×10-6,(c)2.0×10-5,(d)4.0×10-5,(e)6.0×10-5,(f)8.0×10-5,(g)1.0×10-4 mol/L.图14 不同浓度的对苯二酚在GR/GCE上的DPV图(A)与峰电流和对苯二酚浓度的关系(B)Fig.14 DPV for different concentrations of HQ at the GR/GCE(A)and the relationship between the peak currents and concentrations(B)注:浓度分别为(a)4.0×10-6,(b)8.0×10-6,(c)2.0×10-5,(d)4.0×10-5,(e)6.0×10-5,(f)8.0×10-5,(g)1.0×10-4 mol/L.2.4.6 邻苯二酚和对苯二酚的同时测定图15为在p H=5.8的磷酸氢二钠-柠檬酸缓冲溶液为底夜的条件下,裸电极和石墨烯修饰电极分别同时测定2×10-4 mol/L同浓度的邻苯二酚和对苯二酚溶液的DPV图,可知裸电极上出现一个小峰且完全不能将邻苯二酚和对苯二酚分开,而GR/GCE的峰电流明显增加而且能够很好的将邻苯二酚和对苯二酚的峰分开,这表明石墨烯修饰电极对邻苯二酚和对苯二酚的分离效果很好.图15 裸电极(a)和石墨烯修饰电极(b)同时测定邻苯二酚和对苯二酚的DPV图Fig.15 DPV for simultaneous determinnation of HQ and CC with the bare electrode and the GR/GCE in phosphate solution注:浓度为2×10-4 mol/L.图16 不同浓度的HQ和CC同时在GR/GCE上的DPV图(A)以及峰电流与CC(图C)和HQ(图B)的线性关系Fig.16 DPV for different concentrations of HQ and CC at the GR/GCE(A)and the relationship between the peak currents and concentrations of CC(B)and HQ(C)注:浓度分别为(a)4.0×10-5,(b)8.0×10-5,(c)2.0×10-4,(d)4.0×10-4,(e)6.0×10-4,(f)8.0×10-4,(g)1.0×10-3 mol/L.图16为在p H=5.8的磷酸氢二钠-柠檬酸缓冲溶液为底夜的条件下,石墨烯修饰电极对不同溶度的CC和HQ同时测定的DPV图.在4.0×10-5~1.0×10-3 mol/L浓度范围内,CC和 H Q的氧化峰均与浓度成良好的线性关系.对应的线性回归方程:对苯二酚是I pa=1.139 29E-6+0.016 77c;相关系数R=0.999 6;邻苯二酚是I pa=8.810 1E-7+0.017 15c;相关系数R=0.998 4.2.4.7 稳定性和重现性使用石墨烯修饰电极分别平行测定20次1×10-4 mol/L的邻苯二酚和对苯二酚,峰电流基本稳定,邻苯二酚的相对标准偏差为2.5%,对苯二酚的相对标准偏差为2.6%,由此可以说明体系重现性良好,对比新制备的石墨烯修饰电极,分别使用放置一周后,15 d后以及一个月后的电极测定同一浓度的邻苯二酚和对苯二酚溶液,其峰电流无明显变化,表明石墨烯修饰电极具有较长的使用寿命和良好的稳定性,可以用于实际样品的分析测定.2.4.8 干扰实验本实验在已选定的最佳条件下考察了一些废水中常见的离子对2×10-5 mol/L邻苯二酚和对苯二酚溶液进行测定的影响,误差控制在±5%以内,100倍的Ca2+、Al 3+、Zn2+、Fe3+、Fe2+、K+、Ag2+、Cl-、NO3-、SO24-等离子以及VB1、VC、半胱氨酸、赖氨酸、葡萄糖、对硝基苯酚、尿酸等常见酚类物质对邻苯二酚和对苯二酚的测定不造成干扰.2.4.9 模拟水样的测定取叠翠湖中的水样配制不同溶度邻苯二酚和对苯二酚的模拟废水,用 G R/GCE 在-0.2~0.8 V 电位范围内,100 m V/s扫数下测定峰电流,用加标回收法获得模拟废水中邻苯二酚和对苯二酚含量,平行三次,结果见表1和表2.由此可见,测定邻苯二酚的回收率在98.3%~114.3%之间,相对标准偏差在0.2~3.0范围内,对苯二酚的回收率在92.5%~108.6%之间,相对标准偏差在0.6~3.5范围内.表1 不同浓度的邻苯二酚混合液的回收率Table 1 Recoveries of CC with different concentrations样号原始量/(1×10-5 mol/L)加入量/(1×10-5 mol/L)测得量/(1×10-5 mol/L)回收率/% 相对标准偏差/%1 2.0 1.0 3.01 100.9 3.0 2.0 4.28 114.3 1.2 3.0 5.17 105.7 1.1 2 4.0 1.0 4.98 98.3 0.2 2.0 6.21 110.5 1.5 3.0 7.18 105.9 0.3表2 不同浓度的对苯二酚混合液的回收率Table 2 Recoveries of HQ with different concentration样号原始量/(1×10-5 mol/L)加入量/(1×10-5 mol/L)测得量/(1×10-5 mol/L)回收率/% 相对标准偏差/%1 2.0 1.0 2.92 92.5 2.8 2.0 4.02 108.6 1.1 3.0 5.07 102.10.7 2 4.0 1.0 5.05 104.6 3.5 2.0 6.03 101.3 1.0 3.0 6.89 96.5 0.6致谢感谢国家自然科学基金委的资助(国家自然科学基金21075096,21275113).参考文献:[1]Novoselov K S,Geim A K.The rise of graphene[J].Nat Mater,2007,6:183-191.[2]Lee C G,Wei X D,Jeffrey W K,et al.Measurement of the elastic properties and intrinsic strength of monolayer graphene[J].Science,2008,321(5887):385-388.[3]Balandin A A,Ghosh S,Bao W Z,et al.Superior thermal conductivity of single-layer graphene[J].Nano Letters,2008,8(3):902-907.[4]Lu C H,Yang H H,Zhu C L,et al.A Graphene platform for sensing biomolecules[J].Angew Chem Int Ed,2009,48(26):4785-4787.[5]Zhou M,Zhai Y M,Dong S J.Electrochemical biosensing based on reduced graphene oxide[J].Anal Chem,2009,81:5603-5613.[6]Shan C S,Yang H F,Han D X,et al.Water-Soluble graphene covalently functionalized by biocompatibe polylysine[J],Anal Chem,2009,81:2378-2382.[7]Fu C L,Yang W S,Chen X,et al.Direct electrochemistry of glucose oxidase on a graphite nanosheet-Nafion composite film modified electrode [J].Electrochem Commun,2009,11(5):997-1000.[8]Wang Y,Li Y M,Tang L H,et al.Application od graphenemodified electrode for selective detection of dopamine[J],Electrochem Commun,2009,11:889-892.[9]Alwarappan S,Erdem A,Liu C,et al.Probing the electrochemical properties of graphene nanosheets for biosensing application[J],J Phys Chem C,2009,113:8853-8857.[10]Shang N G,Papakonstantinou P,Mc Mullan M,et al. Marchetto -Free efficient growth,orientation and biosensing properties of multilayer graphene nanoflake films with sharp edge planes [J].Adv Funct Mater,2008,18:3506-3514.[11]Tang L H,Li Y M,Feng H B,et al.Preparation structure and electrochemical properties of graphene modified electrode[J].Adv Mater,2009,19:2782-2789.[12]李强,张建斌,霍天瑞,等.对苯二酚合成过程中酚醌物质的气相色谱法分析[J].广州化工,2011,39(1):104-106.[13]王微宏,喻晓峰,文莉.紫外分光光度法同时测定苯酚、邻苯二酚、对苯二酚[J].中国现代医学杂志,2002,12(10):86-88.[14]李淮芬,谢成根,宗佳佳,等.同步荧光法同时测定苯二酚中邻苯二酚和对苯二酚[J].冶金分析,2009,29(9):31-35.[15]杜建中,梁风颜,谭国兵.双波长比值法测定苯二酚异构体的含量[J].福建分析测试,2009,18(12):31-35.[16]耿玉珍,刘葵,刘连伟.吸光度比值导数法同时测定苯酚、邻苯二酚和对苯二酚[J].分析化学研究简报,1997,9(25):1024-1026.[17]李江,李容,李永强,等.BPA 在 Na-MMT-CMC/GCE修饰电极上的电化学行为与检测[J].分析测试学报,2008,27(7):766-768.[18]Du H J,Ye J S,Zhang J Q,et al.Graphene nanosheets modified glassy carbon electrode as a highly sensitive and selective voltammetric sensor for rutin[J].Electroanailsis,2010,10,22(20):2399-2406.[19]杨平,李兰芳,蔡惠,等.双酚A在聚茜素红/碳纳米管电极上的伏安行为[J].武汉工程大学学报,2010,32(11):18-21.[20]蔡惠,廖华玲,刘义,等.对甲基本酚在PLYS/TiO2-CS修饰电极上的电化学行为[J].武汉工程大学学报,2011,33(12):13-17.[21]Hrapovic S,Liu Y L,Male K B,et al.,Electrochemical Biosensing Platforms Using Platinum Nanoparticles and Carbon Nanotubes [J].AnalChem,2004,76(4):1083-1088.[22]Yang M H,Yang Y H ,Liu Y L,et al.,Platinum Nanoparticles-Doped Sol-gel/Carbon Nanotubes composite Electrochemical Sensors and biosensors[J].Bioelectron,2006,2(17):1125-1131.。

quechers-气相色谱-串联质谱法同时测定茶叶中11种不同类别农药残留

quechers-气相色谱-串联质谱法同时测定茶叶中11种不同类别农药残留

江苏预防医学2019年11月第30卷第6期Jiangsu J Prev Med,Nov.,2019,Vol.30,No.6•601••专题论著•QuEChERS-气相色谱-串联质谱法同时测定茶叶中11种不同类别农药残留潘春燕I,和佳鸳I,尹国浩2,蒲彦利1,陶俊杰I,易承学I,徐虹I1.镇江市疾病预防控制中心,江苏镇江212000;2.广州市药品检验所摘要:目的建立同时检测茶叶样品中11种常用农药残留的QuEChERS■气相色谱-串联质谱法(GC-MS/MS)。

方法采用QuEChERS法,以乙睛为提取液,N-丙基乙二胺为净化剂,结合GC-MS/MS仪,以多反应监测(MRM)模式检测,外标法定量。

计算该方法的线性范围、检出限、定量限、回收率和精密度,并对市售茶叶样品进行11种农药残留的检测。

结果采用无水硫酸钠脱水,建立QuEChER&GC-MS/MS法检测11种农药残留,在一定质量浓度范围内线性关系良好,相关系数r均>0.997,方法检出限0.3~2.4“g/kg,定量限1.0〜&0“g/kg,加标回收率为60.8%〜94.7%,相对标准偏差(RSDs)均V 13.9%。

检测8份市售茶叶样品,仅1份检出氧化乐果,但远低于规定限值。

结论建立了适用于检测茶叶中11种不同类型的农药残留的QuEChER®气相色谱-串联质谱法,该方法灵敏、高效、便捷,可在有条件的机构进行推广。

关键词:QuEChERS;茶叶;农药残留;气相色谱串联质谱中图分类号:R113文献标识码:A文章编号:1006-9070(2019)06-0601-04Simultaneous determination of11kinds of pesticide residues in tea leaves by QuEChERS gas chromatography-tandem mass spectrometryPAN Chun-yan*,HE Jia-yuan,YIN Gu-ohao>PU Yan-li,TAO Jun-jie,YI Cheng-xue,XU Hong*Zhenjiang Municipal Center for Disease Control and Prevention,J iangsu Zhenjiang212000,China Abstract:Objective To establish a simple and rapid QuEChERS gas chromatography-tandem mass spectrometry(GC-MS/MS)method to determine11kinds of pesticides residues in tea leave samples.Methods The residues were extracted fromtea leaves with acetonitrile and cleaned up by N-propyl ethylenediamine(PSA),which was subjected to by gas chromatography­tandem mass spectrometry analysis under multiple reaction monitoring mode(MRM)and quantification by matrix-match cali­bration curve method.The linear range,limit of detection and quantitation,recovery rate and precision of the method were cal­culated・The11kinds of pesticide residues in tea samples were detected by established method.Results Using anhydrous sodi­um sulfate for dehydration,the linear relationships of11kinds of pesticide residues measured by QuEChERS GC-MS/MS were good in certain concentration ranges*the correlation coefficients r all>0・997,the limits of detection were0・3-2.4ptg/kg,the limits of quantitation were1.0-&0/ig/kg,the spiked recovery rates were60.8%-94.7%,and the relative standard deviations (RSDs)were all<C13・9%.Only1sample of was detected positive for omethoate,the detected concentration was far below the limit.Conclusion The established QuEChERS GC-MS/MS method was sensitive and convenient with high-performance for the determination of11kinds of pesticide residues in tea leaves♦which can be promoted in certain facilities.Key words:QuEChERS;Tea leaves;Pesticide residues;Gas chromatography-tandem mass spectrometry为保障茶叶产品的安全性,以日本和欧盟为代表的茶叶出口地相继出台了严格的法令,规定茶叶中农药的最大残留限量(MRL)m。

SIMULTANEOUS ANALYSIS OF CATIONS

SIMULTANEOUS ANALYSIS OF CATIONS

专利名称:SIMULTANEOUS ANALYSIS OF CATIONS 发明人:SOGA TOMOYOSHI,INOUE YOSHINORI申请号:JP27156187申请日:19871027公开号:JPH01113651A公开日:19890502专利内容由知识产权出版社提供摘要:PURPOSE:To conduct simultaneous analysis of coexistent ions simply and rapidly, by a method wherein alkaline-earth metal ions are separated chromatographically from a solution to be measured, while the part of water is concentrated and alkali metal ions are separated therefrom in the same way. CONSTITUTION:A solution to be measured injected in a metering tube 3g is carried by an eluant in a bath 1a, and cations of an alkaline-earth metal in the solution are separated chromatographically in a separation column 5a. On the occasion, the cations of an alkali metal are eluted early together with water and arrive at an electrical conductivity detector 7 and an ultraviolet absorbance detector 8 in advance through a mixer 6. In response to this arrival, a selector valve 9 is turned ON, and the water flows into a waste vessel 1d through a selector valve 4 and a concentration column 4g. Simultaneously when the detection of the water by the detector 8 is ended, the valve 9 is turned OFF and the water is concentrated and held in the column 4g. From this water, the cations of the alkali metal are separated likewise in a separation column 5b, and the simultaneous analysis of coexistent ions from the eluted solution containing the cations is executed simply and rapidly by the detectors 7 and 8.申请人:YOKOGAWA ELECTRIC CORP更多信息请下载全文后查看。

基于氧化石墨烯复合材料的实验设计

基于氧化石墨烯复合材料的实验设计

基于氧化石墨烯复合材料的实验设计赖婷;朱明芳;林碧敏;陈敏【摘要】通过超声处理将Fe3O4微球颗粒负载在具有大比表面积的氧化石墨烯(Graphene Oxide,GO)表面,成功合成了Fe3O4微球/氧化石墨烯复合物(Fe3O4-GO),并将该复合物应用于有机酚类化合物的测定分析.首先根据Hummers法制备了GO;然后使用溶剂热法制备了粒径200 nm左右的Fe3O4微球;最后用扫描电子显微镜对材料的形貌结构进行探索.结果表明,该合成方法简单有效,制备的复合物能够有效地应用于电化学传感器的构建,并对有机酚类化合物进行检测分析.【期刊名称】《实验室研究与探索》【年(卷),期】2016(035)012【总页数】4页(P26-28,43)【关键词】Fe3O4微球;氧化石墨烯;复合物的合成设计实验【作者】赖婷;朱明芳;林碧敏;陈敏【作者单位】华南农业大学公共基础课实验教学中心,广东广州510642;广东药学院药科学院,广东广州510006;华南农业大学公共基础课实验教学中心,广东广州510642;华南农业大学公共基础课实验教学中心,广东广州510642【正文语种】中文【中图分类】O614.81+1实验教学是培养创新人才的重要环节,大部分高校对本科生开设的实验主要是基础实验,是为了验证课本上已有的理论知识,只能起到巩固理解书本知识的作用,限制了学生的创新能力的发展[1]。

因此,国内部分高校的实验教学经过逐步改革已在基础实验课程以外,另开设了一些大学生创新性实验项目。

以“教学研究型大学”为定位目标的华南农业大学一直注重本科生科研素质和创新实践能力,近年来在全校多个院系里开展了“大学生创新性实验计划项目”。

这些创新性实验项目既可以有效地弥补基础实验教学的不足,也进一步提高了我校学生综合素质,培养学生实践能力、创新意识和团队精神[2-4]。

近几十年,无机纳米材料在光学、电化学和能源等领域都有着广泛地应用,但是这些材料在实际应用中常遇到难分离、易团聚等难题,限制了其应用。

电机设计论文..

电机设计论文..

12电机设计论文_电动机论文一、选题的依据及意义现在社会中,电能是使用最广泛的一种能源,在电能的生产、输送和使用等方面,作为动力设备的电机是不可缺少的一部分。

电机在国家经济建设,节约能源、环保和人民生中起着十分重要的作用。

发电机主要用于移动电源、风力发电、小型发电设备中;电动机在生产和交通运输中得到广泛使用,电动机主要用于驱动水泵、风机、机床、压缩机、冶金、石化、纺织、食品、造纸、建筑、矿山等机械产品上。

随着科学技术的不断创新和工农业的迅猛发展,电气化与自动化水平不断提高,国民经济各部门对异步电动机的需求量日益增加,对其性能,质量,技术经济指标也相应地提出了越来越高的要求。

因此,对异步电动机品种,必须适时实地做出更新与发展,以适应各个新兴工业领域不同的特殊要求,特别是对需求量最大的中小型异步电动机,在保证其质量运行,寿命长和能满足使用要求的同时,进一步节约铜、铁等材料,提高效率和功率因数,以提高其经济技术指标与降低耗电量,是具有十分重要的意义。

由于Y系列异步电动机具有体积小,重量轻,运行可靠,结构坚固耐用,外形美观等特点,具有较高的效率,有良好的节能效果,而且噪音低,寿命长,经久耐用。

作为普遍用于拖动各种机械的动力设备,其用电量在总的电网的总的负荷中占有重要的一席。

Y系列共有两个基本系列、十六个派生系列、九百多个规格,能满足国民经济各部门的不同需要。

所以设计研究三相异步电动机意义重大。

国内外研究现状及发展趋势(含文献综述)1、现状国外公司注重新产品开发,在电机的安全、噪声、电磁兼容等方面很重视。

国外的先进水平主要体现在电机的可靠性高,寿命长,通用化程度高,电机效率不断提高,噪声低,重量轻,电机外形美观,绝缘等级采用F级和H级,而且也考虑电机制造成本的降低等国内虽有部分产品已达90年代初的国际水平,但相当部分的产品可靠性差,重量重,体积大和噪声大,综合水平只相当于80年代初期国际水平,其主要原因是制造工艺落后,关键材料的质量和品种不能满足要求,科研和设计工作没有跟上,科研投入少,新产品开发资金匮乏,企业技术创新能力较弱2、电机行业发展趋势1)企业在改造中求发展企业要自己选准位置,立足生求,真抓实干,稳步发展。

糠醛的电化学聚合

糠醛的电化学聚合

糠醛的电化学聚合付艳辉;王立世【摘要】变压器油中糠醛的含量是预测变压器故障的重要参数.为了验证在乙腈溶剂中检测糠醛的可行性,以乙腈为溶剂,高氯酸钠和氢氧化钠为支持电解质,在0.5~2.3 V电位范围内,采用循环电压-电流法,使糠醛在玻碳电极上形成致密的聚合物膜.聚合物膜在波长约460 nm处有明显的可见光吸收,随着溶液中糠醛浓度的增大和扫描圈数的增加,聚合物膜在此处波长下的吸光度增大.实验结果表明,此法用于检测糠醛不太理想.【期刊名称】《广东电力》【年(卷),期】2012(025)002【总页数】4页(P9-11,39)【关键词】变压器油;糠醛;电化学聚合;有机相【作者】付艳辉;王立世【作者单位】华南理工大学化学与化工学院,广东广州510640;华南理工大学化学与化工学院,广东广州510640【正文语种】中文【中图分类】TQ251.1变压器在超负荷运转过程中,会导致变压器油变质生成某些成分,通过检测这些成分可以预测变压器失效,其中,糠醛的含量是一个重要的指标[1]。

用电化学方法检测糠醛的方法有脉冲电流检测法[1]和NanoTiO2-CNT复合膜修饰电极检测法[2]等。

糠醛是一种无色或琥珀色的杂环有机化合物,室温下微溶于水,可在酸催化条件下以玉米芯和作物秸秆为原料蒸煮制得,属于可再生资源。

在酸碱催化下,用糠醛聚合形成的糠醛树脂具有良好的耐腐蚀性与热稳定性[3]。

文献[4]对其聚合机理进行了研究。

糠醛树脂是一种具有高度不饱和度、共轭结构的高分子,因此常与半导体Fe2O3或纳米TiO2制备成具有较好光催化性能的复合材料[5-7]。

文献[8]采用界面法合成了聚糠醛纳米球。

文献[9]采用电化学聚合的方法合成了聚3,4-乙撑二氧噻吩薄膜,文献[10]采用此法合成了硫堇聚合膜,文献[11]采用此法电聚合烟酰胺,文献[12]采用此法合成了聚溴酚蓝,文献[13]制备了聚吡咯-聚砜复合膜。

本文采用电聚合的方法合成了糠醛聚合物,并对聚合物膜的形貌和紫外吸收进行分析和研究。

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Simultaneous determination of catecholamines,uric acid and ascorbic acid at physiological levels using poly(N -methylpyrrole)/Pd-nanoclusters sensorNada F.Atta *,Maher F.El-Kady,Ahmed GalalDepartment of Chemistry,Faculty of Science,University of Cairo,Giza 12613,Egypta r t i c l e i n f o Article history:Received 2October 2009Received in revised form 17December 2009Accepted 6January 2010Available online 11January 2010Keywords:Pd nanoclustersElectrochemical sensor Poly(N -methylpyrrole)Catecholamine neurotransmitters Ascorbic acid Uric acida b s t r a c tAn interesting electrochemical sensor has been constructed by the electrodeposition of palladium nanocl-usters (Pd nano )on poly(N -methylpyrrole)(PMPy)film-coated platinum (Pt)electrode.Cyclic voltamme-try,electrochemical impedance spectroscopy (EIS),and scanning electron microscopy were used to characterize the properties of the modified electrode.It was demonstrated that the electroactivity of the modified electrode depends strongly on the electrosynthesis conditions of the PMPy film and Pd nano .Moreover,the modified electrode exhibits strong electrocatalytic activity toward the oxidation of a mix-ture of dopamine (DA),ascorbic acid (AA),and uric acid (UA)with obvious reduction of overpotentials.The simultaneous analysis of this mixture at conventional (Pt,gold [Au],and glassy carbon)electrodes usually struggles.However,three well-resolved oxidation peaks for AA,DA,and UA with large peak sep-arations allow this modified electrode to individually or simultaneously analyze AA,DA,and UA by using differential pulse voltammetry (DPV)with good stability,sensitivity,and selectivity.This sensor is also ideal for the simultaneous analysis of AA,UA and either of epinephrine (E),norepinephrine (NE)or L -DOPA.Additionally,the sensor shows strong electrocatalytic activity towards acetaminophen (ACOP)and other organic compounds.The calibration curves for AA,DA,and UA were obtained in the ranges of 0.05to 1mM,0.1to 10l M,and 0.5to 20l M,respectively.The detection limits (signal/noise [S/N]=3)were 7l M,12nM,and 27nM for AA,DA,and UA,respectively.The practical application of the modified electrode was demonstrated by measuring the concentrations of AA,DA,and UA in injection sample,human serum,and human urine samples,respectively,with satisfactory results.The reliability and stability of the modified electrode gave a good possibility for applying the technique to routine anal-ysis of AA,DA,and UA in clinical tests.Ó2010Elsevier Inc.All rights reserved.Catecholamines are a class of neurotransmitters,and their detection in the human body has been of great interest to neurosci-entists.They include dopamine (DA),1epinephrine (E),and norepi-nephrine (NE)and play important roles in various biological,pharmacological,and physical processes [1].They are widely distrib-uted in the mammalian central nervous system for message transfer [2].DA,ascorbic acid (AA),and uric acid (UA)are compounds of great biomedical interests,playing determining roles in human metabo-lism.DA is one of the crucial catecholamine neurotransmitters thatplay an important role in the function of central nervous,renal,hor-monal,and cardiovascular systems [3].Thus,a loss of DA-containing neurons may lead to neurological disorders such as Parkinsonism and schizophrenia [4].AA is present in both animal and plant king-doms,is a vital vitamin in human diet,and is very popular for its antioxidant properties.It has been used for the prevention and treat-ment of common cold,mental illness,infertility,and cancer and in some clinical manifestations of human immunodeficiency virus (HIV)infections [5].UA is the primary end product of purine metab-olism.The extreme abnormalities of UA levels in the body are symptoms of several diseases,including gout,hyperuricemia,and Lesch–Nyan disease [6].Therefore,simultaneous detection of DA,AA,and UA is a challenge of critical importance not only in the field of biomedical chemistry and neurochemistry but also for diagnostic and pathological research.However,the simultaneous determina-tion of AA,DA,and UA at conventional solid electrodes (carbon and metal)usually struggles because they undergo an overlapping oxidation potential and electrode fouling takes place due to the adsorption of oxidation products [7].Therefore,it is essential to develop simple and rapid methods for their determination in routine0003-2697/$-see front matter Ó2010Elsevier Inc.All rights reserved.doi:10.1016/j.ab.2010.01.001*Corresponding author.Fax:+200235727556.E-mail address:nada_fah1@ (N.F.Atta).1Abbreviations used:DA,dopamine;E,epinephrine;NE,norepinephrine;AA,ascorbic acid;UA,uric acid;HIV,human immunodeficiency virus;Ppy,polypyrrole;ssDNA,single-stranded DNA;PMPy,poly(N -methylpyrrole);PMPy/Pdnano,PMPy modified with palladium nanoclusters;ECP,electronically conducting polymer;CV,cyclic voltammetry;Pt,platinum;DPV,differential pulse voltammetry;ACOP,acetaminophen;MPy,N -methylpyrrole;Bu4NPF6,tetrabutylammonium hexafluoro-phosphate;HPLC,high-performance liquid chromatography;EIS,electrochemical impedance spectroscopy;BE,bulk electrolysis;SEM,scanning electron microscropy;PBS,phosphate-buffered solution;Au,gold;S/N,signal/noise.Analytical Biochemistry 400(2010)78–88Contents lists available at ScienceDirectAnalytical Biochemistryjournal homepage:www.elsev i e r.c o m /l o c a t e /y a b ioanalysis without cross-interferences.Of these,electrochemical methods have received much interest because they are more selec-tive,less expensive,and less time-consuming and can potentially be applied to a real-time determination in vivo[8].There are reports of using polymerfilms[9],nanoparticles[10],self-assembled mono-layers[11],and metal oxide[3]modified electrodes to simulta-neously determine DA and AA and also in the presence of UA.All of the reported modified electrodes have their advantages and limitations.Polypyrrole(Ppy)is one of the most extensively used conduct-ing polymers in the design of bioanalytical sensors[12].Versatility of this polymer is determined by a number of properties:redox activity[13],ion exchange and ion discrimination capacities[14], electrochromic effect depending on electrochemical polymeriza-tion conditions and charge/discharge processes[15],strong absorptive properties toward gases[16],proteins[17],DNA[18], catalytic activity[19],corrosion protection properties[20],and the like.Most of these properties are dependent on the synthesis procedure[21].Ppy may be electrochemically generated and deposited on the conducting surfaces.This technique is success-fully exploited for development of various types of electrochemical sensors and biosensors.In this respect,several major directions are straightforward:(i)catalytic sensors based on immobilized en-zymes[22],(ii)immunosensors based on immobilized affinity exhibiting proteins[23],(iii)DNA sensors based on covalently immobilized and/or entrapped single-stranded DNA(ssDNA)[24], and(iv)affinity sensors based on molecularly imprinted polymers [25].Nowadays,this polymer becomes one of the major tools for nanobiotechnological applications[26].Various approaches have been considered for the synthesis of Ppy,including chemical and electrochemical methods[27].It was reported that the catalytic activity of Ppyfilms depends on the synthesis conditions[21,27]. In our report,potentionstatic(controlled potential electrolysis) and potentiodynamic(cyclic voltammetry)techniques were used to synthesize poly(N-methylpyrrole)(PMPy)films,and their activ-ities were tested in the electrooxidation of the compounds of study.PMPy has attracted attention as a possible alternative to PPy for technological applications in spite of its lower conductivity[28].A step forward with respect to‘‘simple”modification with pris-tine conducting polymers consists in the inclusion of metal func-tionalities inside the polymeric matrix to further increase the performances of the resulting composite material.In particular, inclusion of noble metal nanoparticles,whose catalytic properties are well known[20],constitutes one of the most interesting possi-bilities.Similar composites based on polypyrrole and polyaniline have been reported recently[29],although a precise definition of the structure and properties of the material is far from being achieved exhaustively.Here we report the synthesis,characterization,and sensing applications of a composite material based on PMPy modified with palladium nanoclusters(PMPy/Pd nano).The aim of the develop-ment of the composite material is to improve the electrocatalytic properties of the simple polymeric electrode coating.Several pro-cedures have been employed to prepare metal-supported nanopar-ticles on different carbon supports and electronically conducting polymers(ECPs)[30];of these,electrochemical deposition is an efficient method for the preparation of metal nanoparticles.It is widely used with different strategies/methodologies such as cyclic voltammetry(CV)[31],potential step deposition[32],and double pulse[33].Among these,potential step deposition provides a tool tofine-tune the amount of metal deposited,the number of metallic sites,and their size.Various electrochemical methods have been described for the preparation of ECP/metal nanoparticles,but the most popular approach is the deposition of metal nanoparticles onto electrodes previously coated with ECPfilms[34].Moreover,the methods of formation of the polymerfilm and deposition of metal nanoparticles have a strong impact on the characteristics of the polymer/metal nanoparticle composites and the possible synergistic effects between the dispersed metal nanoparticles and polymerfilm[10–14].For these reasons,we explored how these factors affect the composite-modified electrode.In the current study,PMPy/Pd nano composite-modified platinum (Pt)electrode was used for the simultaneous determination of cat-echolamines,UA,and AA.The electrochemical behaviors of these species at our modified electrode were investigated using CV and differential pulse voltammetry(DPV)techniques.Based on the dif-ferent electrocatalytic activities of the modified electrode toward AA,DA,and UA,a sensitive and selective method for their simulta-neous determination was established.The detection of AA in injec-tion samples,UA in human urine,and DA in human serum was finally demonstrated as real sample applications.Furthermore,this work addresses the electrocatalytic properties of PMPy/Pd nano to-ward the oxidation of acetaminophen(ACOP),which is commer-cially known as paracetamol,as well as some organic compounds.ACOP is an antipyretic and analgesic drug widely used worldwide for the relief of mild to moderate pain associated with headache,backache,arthritis,and postoperative pain.Therefore,its determination is of importance as well.Materials and methodsChemicals and reagentsAll chemicals were used as received without further purification except N-methylpyrrole(MPy,distilled under rotary evaporation prior to use).MPy,tetrabutylammonium hexafluorophosphate (Bu4NPF6),acetonitrile(high-performance liquid chromatography [HPLC]grade),hydroquinone,catechol,DA hydrochloride,E,NE, L-DOPA,methyl-L-DOPA,p-aminophenol,acetaminophen,AA,UA,tryptophan,cysteine,tyrosine,tyramine,serotonin hydrochloride, glucose,sulfuric acid,sodium chloride,potassium chloride,calcium chloride,and magnesium chloride were supplied by Aldrich Chem-ical(Milwaukee,WI,USA).Palladium(II)chloride(Scherimg Kaul Paum,Berlin,Germany)was also used.Aqueous solutions were prepared using doubly distilled water.Electrochemical cells and equipmentElectrochemical polymerization and characterization were car-ried out with a three-electrode/one-compartment glass cell.The working electrode was Pt disk(diameter=1.5mm).The auxiliary electrode was in the form of6.0cm Pt wire.All of the potentials in the electrochemical studies were referenced to Ag/AgCl(3.0M NaCl)electrode.Working electrode was mechanically polished using alumina(2l m)/water slurry until no visible scratches were observed.Prior to immersion in the cell,the electrode surface was rinsed thoroughly with distilled water and dried.Other disk electrodes were used:gold(diameter=1.5mm)and glassy carbon (diameter=3mm).All experiments were performed at25°C.The electrosynthesis of the polymers and their electrochemical characterization were performed using a BAS-100B electrochemi-cal analyzer(Bioanalytical Systems[BAS],West Lafayette,IN, USA).Electrochemical impedance spectroscopy(EIS)measure-ments were performed using a Gamry-750system and a lock-in amplifier that were connected to a personal computer.The data analysis software was provided with the instrument and applied nonlinear least squaresfitting with the Levenberg–Marquardt algorithm.All impedance experiments were recorded between 0.1Hz and100kHz with an excitation signal of10mV amplitude.Nanoclusters-polymer sensor for neurotransmitters/N.F.Atta et al./Anal.Biochem.400(2010)78–8879A Jeol JSM-T330A instrument was used to obtain the scanning elec-tron micrographs of the differentfilms.Electropolymerization of MPyMPy was electropolymerized from a monomer solution contain-ing0.05M MPy/0.05M Bu4NPF6/acetonitrile using two electro-chemical methods.In thefirst method(bulk electrolysis[BE] method),the potential applied between the Pt disk working elec-trode and the reference(Ag/AgCl)was held constant at+1.8V for 30s and the electrode is called Pt/PMPy(BE).In the second method (CV method),the potential is changed with time,namely 50mV sÀ1,between two potential limits(E i$À0.1V and E f$+1.8V)for10cycles and the electrode is called Pt/PMPy(CV).For all polymerfilms,the thickness was controlled by the amount of charge consumed during the electropolymerization step.Therefore,assuming100%current efficiency during the elec-trochemical conversion,it is possible to use the following empirical equation[35]to roughly estimate thefilm thickness:L¼m eÁjÁt=S;ð1Þwhere L is the thickness(cm),m e is the electrochemical equivalent (mg CÀ1),j is the current density(mA cmÀ2),t is the time(s),and S is the density(g cmÀ3).The polymerfilm was alternatively formed using the BE and CV methods;the total charges passed were approximately1Â104l C and0.99Â104l C,respectively,and the thicknesses were calculated to be approximately200and198nm, respectively.Because100%current efficiency might not be ob-tained,this represents the maximumfilm thickness possible and is constant in all experiments.Preparation of PMPy/Pd nano composite electrodesThe electrodeposition of Pd nano on the polymerfilm was re-ported in our previous work[36].Briefly,a polymerfilm is pre-pared by either the BE or CV method and is washed with doubly distilled water.This was followed by the electrochemical deposi-tion of Pd nano on the polymerfilm from a solution of2.5mM PdCl2 in0.1M HClO4by applying a double potential step(method I)or a CV program(method II)to the polymer.The double potential step conditions are E i=À0.05V,D t i=30s,E f=+0.01V,and D t f=300s, and the electrode formed in this way is indicated Pt/PMPy/Pd nano(I). In the CV method,the electrode is cycled betweenÀ0.25and +0.65V at a scan rate of50mV sÀ1for25cycles,and the electrode formed in this way is indicated Pt/PMPy/Pd nano(II).Furthermore,the surface coverage(C)of Pd nano has been calcu-lated using the following equation:C¼Q=nFA;ð2Þwhere Q is the charge,n is the number of electrons involved in the electron transfer process(n=2),F is the Faraday constant,and A is the geometric area of the Pt(0.0176cm2)[37].The surface coverage (C)of Pd nano was estimated by integrating the charge(Q)of catho-dic peak current of Pd nano at a scan rate of0.02V/s.The surface cov-erages of Pd nano were approximately 5.1Â10À9and 5.2Â10À9 mol cmÀ2for the electrodeposition with methods I and II, respectively.Results and discussionResults of electropolymerization of MPyThe charge time and current time transients obtained during the electropolymerization of MPy by the BE method(see Fig.S1a in supplementary material)indicate a slow charge transfer due to the previously formed polymer layer that affects the subsequent formation and thickening of PMPy.(See supplementary material for details behind this conclusion.)Repeated cyclic voltammograms(Fig.S1b)obtained during the electropolymerization of MPy show relative decay in the current of the oxidation process that is responsible for the polymerfilm thickening(cf.the current of thefirst cycle with that of the last cy-cle).The decrease in current reflects the insulating character of the film formed during thefirst few cycles as the number of scans in-creases.It was mentioned earlier that a disadvantage of pyrrole is the presence of available sites for coupling in the b-position of the ring duringfilm propagation[38].Consequently,a break in conju-gation will result and a decrease infilm conductivity is observed [39].Electrochemistry of catecholamines at PMPy-modified electrodes prepared under different electrochemical conditionsIt has been mentioned that the method of polymerization of Ppy has a strong impact on the morphology and catalytic activity[40] of polymer-modified electrodes.PMPyfilms were prepared using two different methods(CV and BE)and their activities toward the electrooxidation of DA were tested.Fig.S2in the supplementary material depicts the cyclic voltam-mograms of DA at bare Pt,Pt/PMPy(BE),and Pt/PMPy(CV).As can be seen,DA exhibit a very weak CV peak response with D E p values of 333and227mV at bare Pt and Pt/PMPy(BE)electrodes,respec-tively.But at Pt/PMPy(CV),the peak current increased and the peak potential shifted negatively to536mV.The voltammograms show a couple of reversible and well-behaved redox peaks with a D E p of only66mV.Moreover,the difference in the electrochemical behavior between the two polymer-modified electrodes is highly manifested in the other catecholamines(E and NE),where hardly any signals were observed at Pt/PMPy(BE)(Table1).This noticeable difference in the electrocatalytic activity of the two polymerfilms prepared under different electrochemical condi-tions may be explained by the surface morphology analysis(Fig.1). The polymerfilm of Pt/PMPy(BE)is compact and relatively smooth with lower surface roughness.However,Pt/PMPy(CV)isfluffy with higher surface roughness,and that means higher surface area. Thus,the difference in electrocatalytic activity between the poly-mer-modified electrodes may be attributed to the larger surface area of Pt/PMPy(CV).Modification of PMPy with Pd nanoclustersCharacterization of Pd nano-modifiedfilm electrodesFig.2shows the cyclic voltammograms of Pd nano-modified elec-trodes tested in0.1M H2SO4.Here the voltammograms show the characteristic current features of Pd reduction(0.25V),Pd oxide formation(0.95V),and hydrogen adsorption and desorption(0to À0.2V)processes.On scanning the potential in the negative direc-tion,Pd nano are deposited on the electrode surface and the peak at approximatelyÀ0.1V shows the reduction process of protons to hydrogen,which are adsorbed on the Pd nano surface.This reduction peak confirms the hydrogen adsorption process on the Pd nano sur-face.During the positive potential scanning process,the peak at À0.05V appears to be due to the oxidation of hydrogen atoms.In the next step,the deposited Pd nano are further oxidized to Pd2+to form a Pd oxide layer(0.95V)on the electrode surface.These peaks do not appear at Pt and Pt/PMPy(BE)electrodes.The formed Pd oxi-des are further reduced on the negative-going scans,leading back to metallic Pd with hydrogen adsorption process.These observa-tions clearly suggest the formation of Pd nano and are consistent with previous reports[41].80Nanoclusters-polymer sensor for neurotransmitters/N.F.Atta et al./Anal.Biochem.400(2010)78–88Effect of method of polymerization of MPy on electroactivity of PMPy/Pd nano composite electrodeFig.S3in the supplementary material shows how changing the method of polymer film formation could affect the electroactivity of Pt/PMPy/Pd nano electrodes.The results indicate that Pt/PMPy (BE)/Pd nano(II)electrode shows lower oxidation potential,high-er peak currents,and lower peak separation;thus,the redox reac-tion of DA is thermodynamically and kinetically more favorable at this electrode when compared with Pt/PMPy (CV)/Pd nano(II)elec-trode,which shows very high capacitive current.Thus,although Pt/PMPy (CV)is more electroactive when compared with Pt/PMPy (BE),bringing Pd nano to the polymer film changes this picture because the behavior of the composite electrode is a synergic phe-nomenon and is independent of the individual behavior of the polymer layer and Pd nano .In fact,the electroactivity of PMPy/Pd nano depends on the way Pd nano interact with the polymer film.Taking a look at the morphology of the PMPy/Pd nano composites may help us to explain the unexpected higher electroactivity of Pt/PMPy (BE)/Pd nano(II)electrode.Scanning electron microscropy (SEM)images (Fig.1)show that the method of polymerization affects thesize and distribution of Pd nano .Pt/PMPy (BE)/Pd nano(II)exhibits spher-ical Pd nanoclusters with a homogeneous size distribution,whereas Pt/PMPy (CV)/Pd nano(II)exhibits smaller Pd nanoclusters but the particle sizes are not homogeneous.A further explanation of the effect of the method of formation of the polymer film on the electroactivity of PMPy/Pd nano is provided in the EIS study in a later subsection.Electrochemistry of catecholamine neurotransmitters at PMPy/Pd nano electrodes with emphasis on effect of deposition of Pd nanoclusters In this subsection,the effects of the presence of Pd nano as well as the method of their deposition on the electroactivity of PMPy electrodes and the electrochemistry of catecholamine neurotrans-mitters are presented using CV.Fig.S4in the supplementary material shows cyclic voltammograms for DA at PMPy films mod-ified with Pd nano electrodeposited with different methods and Pd nano directly electrodeposited over Pt substrate.From Fig.S4a ,it can be seen that bare Pt and Pt/PMPy (BE)electrodes exhibit poorly defined oxidation peaks with large peak-to-peak separa-tion at 664and 614mV,respectively.Moreover,the cathodicTable 1Summary of CV results obtained at polymer and Pd nano -modified polymer electrodes in 5mM analyte/0.1M H 2SO 4at a scan rate of mVs ÀpoundPt/PMPy Pt/PMPy (BE)/Pd BE a CV a I bII bE pa (mV)I pa (l A)E pa (mV)I pa (l A)E pa (mV)I pa (l A)E pa (mV)I pa (l A)Hydroquinone 49682.645047.7456150.1461241.5Catechol 610165.2560124.0546191.0550327.2Dopamine61439.353667.2549112.3553290.4Methyl-L -DOPA 58554.056850.756297.4566261.6Epinephrine –c –c 56740.356184.8564216.8Norepinephrine –c –c 57144.355489.1557194.1p -Aminophenol –c –c 55548.952074.5533221.6Acetaminophen 81082.272260.9699199.3698290.3Ascorbic acid–c–c31453.029574.8296120.7Note.The deposition of Pd nano on the polymer film lowers the oxidation potential (thermodynamic action)and raises the peak currents (kinetic action).For the CV results at Pt and Pd nano -modified Pt electrodes,see our previous report [36].aMethod of formation of the polymer film.bMethod of deposition of Pd nanoclusters.cNo signalobserved.Fig.1.Schematic showing two-step process for the modification of Pt electrode.In the first step,a polymer film is electrodeposited on Pt electrode using two electrochemical methods (BE and CV).In the second step,Pd nano are deposited on the polymer film using two approaches (double potential step [I]and CV program [II]).The notation of every electrode is described.SEM micrographs for all cases are shown.See text for details.The SEM image of Pt/PMPy (CV)/Pd nano(I)is omitted because of its low electroactivity.Nanoclusters-polymer sensor for neurotransmitters /N.F.Atta et al./Anal.Biochem.400(2010)78–8881peak current is much smaller than the anodic peak current.It is clear that the electron transfer kinetics of DA at the bare Pt and Pt/PMPy electrodes are sluggish [42].On the other hand,the re-dox peaks at the Pt/PMPy (BE)/Pd nano(I)and Pt/PMPy (BE)/Pd nano(II)electrodes are reversible with the anodic peaks shifted negatively to 549and 553mV,respectively,and the peak currents increased significantly.Similarly,voltammograms of DA were recorded at bare Pt,Pt/Pd nano(I),and Pt/Pd nano(II)(Fig.S4b ).Pd nano -modified Pt electrodes exhibited similar catalytic behavior for the oxidation of DA.DA demonstrated an oxidation peak at 664mV at bare Pt,whereas the anodic peaks shifted negatively to 530and 534mV at Pt/Pd nano(I)and Pt/Pd nano(II),respectively.Furthermore,the re-dox signals showed enhanced peak currents,indicating an improvement in the electrode kinetics when the Pt/Pd nano elec-trodes are used.Table 1summarizes the CV results for catecholamine neuro-transmitters (DA,E,and NE),precursor to catecholamines (methyl-L -DOPA),polyhydroxy phenyls (hydroquinone and cate-chol),p -aminophenol,acetaminophen,and AA at the different elec-trodes.At the Pd nano -modified electrodes,all of the compounds showed a clear negative shift in the oxidation peak potentials accompanied by a significant increase in the anodic peak current.Thus,the remarkable enhancement in current response followed by a drop in peak potential provides clear evidence of the catalytic effect of Pd nano that acts as a promoter to enhance the electrochem-ical reaction,considerably accelerating the rate of electron transfer.The remarkably enhanced signal at Pt/PMPy/Pd nano electrodes is attributed to both of the surface-modified PMPy film and Pd nano .The composite plays an important role in accelerating the electron transfer at lower potentials and increasing the oxidation current.A plot of the oxidation peak current (I pa )versus the square root of scan rate (v 1/2)for the Pd nano -modified electrodes yields a straight line in the scan rate range from 10to 200mV s À1(see Fig.S4inset).Such behavior suggests that the electron transfer process at the Pd nano -modified electrodes is diffusion controlled,and this is favor-able for quantitative applications [43].An SEM picture of Pt/PMPy (BE)/Pd nano(I)electrode (Fig.1F)re-veals that the clusters of electrodeposited Pd exist as nanocrystal-lites (dendrite structures)with a preferential growth in certain crystallographic directions.This observation shows that the elec-trodeposition of Pd nano leads to the formation of sub-microcrystal-lites with smaller grains (in the nano range).EIS studiesThe EIS technique is used to study the capacitance and resis-tance of PMPy/Pd nano electrodes.Moreover,the electrochemical system studied is compared with an ‘‘equivalent circuit”that uses some of the conventional circuit elements,namely resistance,capacitance,diffusion,and induction elements.The data are repre-sented as a relation between the impedance and the frequencies,namely the Bode plot.In all cases,the experimental data are com-pared with the equivalent circuit models.Thus,it is anticipated that the changes in the conditions of the experiments,as willbeFig.2.Characterization of Pd nano -modified electrodes.Cyclic voltammograms were obtained in 0.1M H 2SO 4solution at the respective electrodes with a scan rate of 20mV s À1.The voltammograms show the characteristic current features of Pd reduction (0.25V),Pd oxide formation (0.95V),and hydrogen adsorption and desorption (0to À0.2V)processes.See text fordetails.Fig.3.Results of EIS.(A)Equivalent circuit used in the fit procedure of the impedance spectra.(B,C)Bode plot of impedance spectra for Pt/PMPy (BE)/Pd nano(II)(B)and Pt/PMPy (CV)/Pd nano(II)(C),all tested in 5mM DA/0.1M H 2SO 4.The method of preparation of the polymer film was reflected on the electrochemical impedance properties of the PMPy/Pd nano composite-modified electrodes.See text for details.82Nanoclusters-polymer sensor for neurotransmitters /N.F.Atta et al./Anal.Biochem.400(2010)78–88。

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