Adsorption behaviors of acetaminophen onto sediment in the Weihe River,Shaanxi,China
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降解对乙酰氨基酚的好氧颗粒污泥体系高效降解菌株功能化模式研究的开题报告一、选题背景及意义对乙酰氨基酚是一种常见的解热镇痛药,其含量在生活污水中比较普遍。
对乙酰氨基酚具有一定的毒性,对于人体健康和环境安全具有潜在的危害。
因此,对乙酰氨基酚的处理和降解一直是环境保护领域的重要研究方向之一。
当前,常规的处理对乙酰氨基酚的方法主要有活性炭吸附、紫外光催化等,这些方法不仅成本高,而且效率较低,无法满足潜在的环境保护需求。
因此,开展对乙酰氨基酚的好氧颗粒污泥体系高效降解菌株功能化模式研究,有重要的理论价值和应用前景。
二、研究目标本研究旨在筛选一株高效降解对乙酰氨基酚的微生物,并构建好氧颗粒污泥体系,从而实现对乙酰氨基酚的高效降解,并探讨功能化模式。
三、研究内容1.筛选高效降解对乙酰氨基酚的微生物菌株。
2.构建好氧颗粒污泥体系,考察对乙酰氨基酚的去除效果。
3.对颗粒污泥进行形态和结构等的分析。
4.收集和统计颗粒污泥中微生物的信息,探讨颗粒污泥微生物群落的构成规律。
5.探讨功能化模式,评估对乙酰氨基酚降解效果的影响。
四、研究方法1.从污水样品中分离筛选对乙酰氨基酚的高效生物降解菌株。
2.构建好氧颗粒污泥体系,考察对乙酰氨基酚的去除效果,并进行性能评估。
3.采用扫描电镜、荧光显微镜等分析方法对颗粒污泥进行形态和结构等的分析。
4.通过测序和分析等方法,对颗粒污泥微生物群落进行构成分析。
5.探讨功能化模式,评估对乙酰氨基酚降解效果的影响。
五、研究预期成果1.筛选到高效生物降解对乙酰氨基酚的菌株。
2.构建好氧颗粒污泥体系,提高对乙酰氨基酚的去除效果。
3.探讨颗粒污泥微生物群落的构成规律,为后续研究提供理论基础。
4.探讨功能化模式,提高对乙酰氨基酚降解效果,并为相关领域的研究和应用提供指导意见。
5.本研究结果可在环境保护方面具有广泛的应用前景。
六、研究进度安排1.前期准备:2022年6月至2023年3月2.微生物筛选和颗粒污泥构建:2023年4月至2024年3月3.形态和结构等的分析:2024年4月至2025年3月4.微生物群落的构成分析:2025年4月至2026年3月5.功能化模式的探讨与评估:2026年4月至2027年3月6.论文撰写和答辩准备:2027年4月至2028年3月七、参考文献1.张燕莉,张培强,丁永新,等.高效降解对乙酰氨基酚的微生物筛选[J].生物技术通讯,2019,30(9):1363-1368.2.Wu X, Li Y, Liu J, et al. Adsorption behavior and mechanism for removal of acetaminophen from aqueous solution by modified wheat straw[J]. Journal of Environmental Science & Health, Part A, 2019,54(3):244-251.3.Zhu D, Ren N, Lin M, et al. Anaerobic degradation ofacetaminophen by Pseudomonas sp. HPD-2 and its key enzymes[J].Journal of Hazardous Materials, 2012, 241-242: 371-378.。
Journal of Hazardous Materials 181 (2010) 535–542Contents lists available at ScienceDirectJournal of HazardousMaterialsj o u r n a l h o m e p a g e :w w w.e l s e v i e r.c o m /l o c a t e /j h a z m atAdsorptive removal of methyl orange from aqueous solution with metal-organic frameworks,porous chromium-benzenedicarboxylatesEnamul Haque a ,Ji Eun Lee a ,In Tae Jang b ,Young Kyu Hwang b ,Jong-San Chang b ,Jonggeon Jegal c ,Sung Hwa Jhung a ,∗aDepartment of Chemistry,Kyungpook National University,Daegu 702-701,Republic of KoreabResearch Center for Nanocatalysts,Korea Research Institute of Chemical Technology,P.O.Box,107,Yusung,Daejeon 305-600,Republic of Korea cMembrane and Separation Research Center,Korea Research Institute of Chemical Technology,P.O.Box 107,Yusung,Daejeon 305-600,Republic of Koreaa r t i c l e i n f o Article history:Received 8February 2010Received in revised form 8May 2010Accepted 10May 2010Available online 16 May 2010Keywords:Porous chromium-benzenedicarboxylates MOFsMethyl orange DyeAdsorption Removala b s t r a c tTwo typical highly porous metal-organic framework (MOF)materials based on chromium-benzenedicarboxylates (Cr-BDC)obtained from Material of Institute Lavoisier with special structure of MIL-101and MIL-53have been used for the adsorptive removal of methyl orange (MO),a harmful anionic dye,from aqueous solutions.The adsorption capacity and adsorption kinetic constant of MIL-101are greater than those of MIL-53,showing the importance of porosity and pore size for the adsorption.The performance of MIL-101improves with modification:the adsorption capacity and kinetic constant are in the order of MIL-101<ethylenediamine-grafted MIL-101<protonated ethylenediamine-grafted MIL-101(even though the porosity and pore size are slightly decreased with grafting and further protonation).The adsorption capacity of protonated ethylenediamine-grafted MIL-101decreases with increasing the pH of an aqueous MO solution.These results suggest that the adsorption of MO on the MOF is at least partly due to the electrostatic interaction between anionic MO and a cationic adsorbent.Adsorption of MO at various temperatures shows that the adsorption is a spontaneous and endothermic process and that the entropy increases (the driving force of the adsorption)with MO adsorption.The adsorbent MIL-101s are re-usable after sonification in water.Based on this study,MOFs can be suggested as potential re-usable adsorbents to remove anionic dyes because of their high porosity,facile modification and ready re-activation.© 2010 Elsevier B.V. All rights reserved.1.IntroductionRecently,considerable amount of waste water having color has been generated from many industries including textile,leather,paper,printing,dyestuff,plastic and so on [1].Removal of dye mate-rials from water is very important because water quality is greatly influenced by color [1]and even small amount of dyes is highly visible and undesirable.Moreover,many dyes are considered to be toxic and even carcinogenic [1–3].It is difficult to degrade dye materials because they are very sta-ble to light and oxidation [3].For the removal of dye materials from contaminated water,several methods such as physical,chemical and biological methods have been investigated [1,3].Among the proposed methods,removal of dyes by adsorption technologies is regarded as one of the competitive methods because adsorption does not need a high operation temperature and several color-ing materials can be removed simultaneously [1].The versatility∗Corresponding author.Fax:+82539506330.E-mail address:sung@knu.ac.kr (S.H.Jhung).of adsorption,especially with activated carbons,is due to its high efficiency,economic feasibility and simplicity of design [3].Methyl orange (MO)is one of the well-known acidic/anionic dyes,and has been widely used in textile,printing,paper,food and pharmaceutical industries and research laboratories [2].The struc-ture of MO is shown in Scheme 1and the removal of MO from water is very important due to its toxicity [2,3].Harmful MO is selected in this study as a representative acidic dye.Several adsorbents such as ammonium-functionalized MCM-41and layered double hydroxides (LDH)have been studied for the removal of MO dye [4,5].Adsorbents,including activated carbon,made from wastes attract attention to decrease the cost of adsorp-tion [2,6].Agricultural wastes such as lemon [7],banana and orange peel [8]and biopolymers [9]like alginate have also been used.Functionalized adsorbents such as hyper-crosslinked polymers [10]and diaminoethane sporollenin [11]have also been studied.For efficient separation of adsorbent from liquid after adsorption,magnetic particles have also been dispersed/incorporated in the adsorbent [9,12].The thermodynamics parameters of MO adsorption have been studied over various adsorbents [2,5–7,10].In every case,the G0304-3894/$–see front matter © 2010 Elsevier B.V. All rights reserved.doi:10.1016/j.jhazmat.2010.05.047536 E.Haque et al./Journal of Hazardous Materials181 (2010) 535–542Scheme1.is negative for spontaneous adsorption;however H depends on adsorbents[2,5–7,10]and S is generally positive[2,5–7]. The adsorption kinetics has been interpreted with various models [2–10]and the adsorption of MO over MCM-41illustrates that the adsorption process is composed of complex processes like diffusion in surface or mesopore and adsorption on mesopore[4].Moreover, the kinetic constants vary widely depending on the adsorbents [2–10].Metal-organic frameworks(MOFs)are crystalline porous mate-rials which are well known for their various applications[13–20]. The particular interest in MOF materials is due to the easy tunability of their pore size and shape from a microporous to a mesoporous scale by changing the connectivity of the inorganic moiety and the nature of organic linkers[13–15].MOFs are especially inter-esting in thefield of adsorption,separation and storage of gases and vapors[16,19].For example,the storage of hydrogen[16]and carbon dioxide/methane[21]using MOFs has been extensively investigated.The removal of hazardous materials such as sulfur-containing materials has also been studied[22,23].Among the numerous MOFs reported so far,two of the most topical solids are the porous chromium-benzenedicarboxylates (Cr-BDCs)namely MIL-53[24](MIL stands for Material of Insti-tute Lavoisier)and MIL-101[25,26],which are largely studied for their potential -53with a chemical formula of Cr(OH)[C6H4(CO2)2]·n H2O,has an orthorhombic structure and pore volume of0.6cc/g[24].MIL-101,Cr3O(F/OH)(H2O)2[C6H4(CO2)2], has a cubic structure and huge pore volume of1.9cc/g[25,26].The pore sizes of MIL-53and MIL-101are around0.85and2.9–3.4nm, respectively[24–26].MIL-53is very interesting due to the breath-ing effect[27],and has been widely studied for adsorption[23]and drug delivery[20,28].MIL-101is a very important material due to its mesoporous structure and huge porosity,and is widely studied for adsorption[29],catalysis[30]and drug delivery[20,28].However,so far,there has been no report of the use of MOFs including Cr-BDCs in the removal of dye materials.In this work,we report,for thefirst time,the results of the adsorption of MO over MOFs,especially well-studied Cr-BDCs,to understand the charac-teristics of adsorption and possibility of using MOFs as adsorbents for the removal of dye materials from waste water.2.ExperimentalThe Cr-BDCs such as MIL-53and MIL-101were prepared follow-ing the reported methods[24–26,31,32].Ethylenediamine-grafted MIL-101(ED-MIL-101)was obtained by grafting ethylenediamine according to the method reported earlier[26,30].The protonated ED-MIL-101(PED-MIL-101)was obtained by acidification of ED-MIL-101with0.1M HCl solution at room temperature for6h. Activated carbon was purchased from Duksan chemical company (granule,size:2–3mm).The textural properties of the adsor-bents were analyzed with a surface area and porosity analyzer (Micromeritics,Tristar II3020)after evacuation at150◦C for12h. The surface area,pore volume and average pore size were calcu-lated using the nitrogen adsorption isotherms.An aqueous stock solution of MO(1000ppm)was prepared by dissolving MO(molecular formula:C14H14N3NaO3S,molecu-lar weight:327.34,Daejung Chemicals co.Ltd.,Korea)in deionized water.Aqueous MO solutions with different concentrations of MO (5–200ppm)were prepared by successive dilution of the stock solution with water.The MO concentrations were determined using the absorbance(at464nm)of the solutions after getting the UV spectra of the solution with a spectrophotometer(Shimadzu UV spectrophotometer,UV-1800).The calibration curve was obtained from the spectra of the standard solutions(5–50ppm)at a specific pH5.6.Before adsorption,the adsorbents were dried overnight under vacuum at100◦C and were kept in a desiccator.An exact amount of the adsorbents(∼10mg)was put in the aqueous dye solutions (50mL)havingfixed dye concentrations from20ppm to200ppm. The MO solutions(pH:5.6)containing the adsorbents were mixed well with magnetic stirring and maintained for afixed time(10min to12h)at25◦C.After adsorption for a pre-determined time,the solution was separated from the adsorbents with a syringefil-ter(PTFE,hydrophobic,0.5m),and the dye concentration was calculated,after dilution(if necessary),with absorbance obtained using UV spectra.The adsorption rate constant was calculated using pseudo-second or pseudo-first order reaction kinetics[33–35]and the maximum adsorption capacity was calculated using the Lang-muir adsorption isotherm[33,36]after adsorption for12h.To get the thermodynamic parameters of adsorption such as G(free energy change), H(enthalpy change)and S(entropy change) the adsorption was further carried out at35and45◦C.To determine the adsorption capacity at various pHs,the pH of the MO solution was adjusted with0.1M HCl or0.1M NaOH aqueous solution.The used adsorbent was activated with deion-ized water(0.05g adsorbent in25ml water)under ultrasound (Sonics and Materials,USA;Model:VC X750,power:750W,ampli-tude;35%)at room temperature for60min(temperature raised to 65◦C–70◦C after sonification).After separation,the adsorbent was dried and reused for the next adsorption.3.Result and discussion3.1.Adsorption kineticsTo understand the adsorption kinetics,MO was adsorbed at var-ious times up to12h,and the quantity of adsorbed MO is displayed in Fig.1when the initial MO concentration is30-50ppm.As shown in Fig.1,the adsorbed quantity of MO is in the order of acti-vated carbon<MIL-53<MIL-101<ED-MIL-101<PED-MIL-101for the whole adsorption time from any initial MO concentration.The adsorbed MO slightly increases with the initial MO concentration, showing the favorable adsorption at high MO concentration.The adsorption time needed for saturation of the adsorbed amount is in the order of activated carbon>MIL-53>MIL-101>ED-MIL-101>PED-MIL-101(Supplementary data Fig.S1).The adsorption over modified MIL-101s is practically completed in2h,showing the rapid adsorption of MO over the modified MIL-101s.However, the adsorbed amount increases steadily with time over the acti-vated carbon.To compare the adsorption kinetics precisely,the changes of adsorption amount with time are treated with the versa-tile pseudo-second-order kinetic model[33–35]because the whole data during adsorption time can be treated successfully:dq tdt=k2(q e−q t)2(1) or,tq t=1k2q2e+1q et(2)where q e:amount adsorbed at equilibrium(mg/g);q t:amount adsorbed at time t(mg/g);t:adsorption time(h).E.Haque et al./Journal of Hazardous Materials181 (2010) 535–542537Fig.1.Effect of contact time and initial MO concentration on the adsorption of MO over thefive adsorbents:(a)C i=30ppm;(b)C i=40ppm;(a)C i=50ppm.Therefore,the second-order kinetic constant(k2)can be calcu-lated byk2=slope2int erceptwhen the t/q t is plotted against t.Fig.2shows the plots of the pseudo-second-order kinetics of the MO adsorption over thefive adsorbents at threeinitial Fig.2.Plots of pseudo-second-order kinetics of MO adsorption over thefive adsor-bents:(a)C i=30ppm;(b)C i=40ppm;(a)C i=50ppm.dye concentrations.The calculated kinetic constants(k2)and cor-relation coefficients(R2)are shown in Table1.The adsorption kinetic constants for MO adsorption are in the order of activated carbon<MIL-53<MIL-101<ED-MIL-101<PED-MIL-101,similar to the adsorbed quantity(Fig.1).Therefore,PED-MIL-101is the most effective adsorbent for MO removal in the viewpoint of adsorption amount and rate.538 E.Haque et al./Journal of Hazardous Materials181 (2010) 535–542 The adsorption kinetic constants over activated carbon and Cr-BDCs are larger than those over crosslinked polymer[10]andactivated carbon(obtained from agricultural product,Phragmitesaustralis)[3].On the contrary the constants are smaller than theconstants over NH3+-MCM-41,activated carbon(entrapping mag-netic cellulose bead)[12],lemon peel[7]and alginate bead[9].The kinetic constants over activated carbon and Cr-BDCs increaseslightly with increasing the initial MO concentration,showingrapid adsorption in the presence of MO in high concentration.Theincrease of the kinetic constant with increasing initial adsorbateconcentration has been reported too[33,37,38].The kinetic con-stants of adsorption over Cr-BDCs show that the adsorption overPED-MIL-101is the fastest and the adsorption kinetics increaseswith modification of virgin MIL-101.The kinetic constant over PED-MIL-101is around10times greater than that of the activated carbonunder the experimental conditions.The adsorption data were also analyzed using the pseudo-first-order kinetic model[33]:ln(q e−q t)=ln q e−k1t(3)Therefore,thefirst order kinetic constant(k1)can be calculatedbyk1=−slope when the ln(q e−q t)is plotted against t.The plots of the pseudo-first-order kinetics of the dye adsorp-tions over thefive adsorbents at the initial MO concentrations of30–50ppm are shown in Fig.S2(adsorption time is only0–1hfor good linearity[33])and the kinetic constants are displayed inTable S1.Similar to the second-order kinetic constants,the rateconstant generally increases in the order of activated carbon<MIL-53<MIL-101<ED-MIL-101<PED-MIL-101,confirming once againthe most rapid adsorption over PED-MIL-101.However,the lin-earity of thefirst order kinetics is relatively poor(low correlationcoefficients R2).The fast adsorption of MO over MIL-101,compared with theadsorption over MIL-53,is probably due to the large pore size ofMIL-101as the kinetic constant of adsorption generally increaseswith the increasing pore size of a porous material not only inliquid-phase adsorption[39,40]but also in gas phase adsorption[41].However,the kinetic constants of the MIL-101s show that thepore size of the MIL-101s(Table1)does not have any effect on thekinetics of adsorption,suggesting the presence of a specific inter-action between PED-MIL-101or ED-MIL-101and MO because theadsorption kinetic constant increases with increasing pore size ifthere is no specific interaction between adsorbate and adsorbent[39–41].3.2.Adsorption thermodynamicsThe adsorption isotherms were obtained after adsorption forsufficient time of12h,and the results are compared in Fig.3a.Theamount of adsorbed dye is in the order of PED-MIL-101>ED-MIL-101>MIL-101>MIL-53>activated carbon for the experimentalconditions,suggesting the efficiency of the Cr-BDCs,especially PED-MIL-101.As shown in Fig.3b,the adsorption isotherms have beenplotted to follow the Langmuir equation[33,36]:C e q e =C eQ0+1Q0b(4)where C e:equilibrium concentration of adsorbate(mg/L) q e:the amount of adsorbate adsorbed(mg/g)Q0:Langmuir constant(maximum adsorption capacity)(mg/g) b:Langmuir constant(L/mg or L/mol)So,the Q0can be obtained from the reciprocal of the slope of a plot of C e/q e against C e.The Q0for all of the samples is determined from Fig.3b and the values are summarized in Table1.Generally the Q0increases inthe Fig.3.(a)Adsorption isotherms for MO adsorption over thefive adsorbents and(b) Langmuir plots of the isotherms(a).The arrows in(b)show that the y-axis scale of activated carbon is different to that of MOFs.order of activated carbon<MIL-53<MIL-101<ED-MIL-101<PED-MIL-101,and the adsorption capacity of PED-MIL-101is194mg/g. The large adsorption capacity of MIL-101for MO,compared to that of MIL-53,is probably due to the large porosity of MIL-101as the adsorption capacity generally increases with increasing the poros-ity of adsorbents[42,43].So far many adsorbents have been evaluated as candidates for the removal of MO from water and their adsorption capacities have varied widely from2.1to about366mg/g depending on the adsor-bent[1–12].Even though the adsorption capacity of Cr-BDCs is less than that of NH3+-MCM-41[4],LDH[5]and activated carbon(made from an agricultural product,Phragmites australis)[3],its capacity is relatively greater than that of the most adsorbents[1,2,6–12].To shed light on the MO adsorption over Cr-BDCs,the adsorp-tion free energy,enthalpy and entropy change were calculated from the adsorption of MO over PED-MIL-101at various temperatures. Fig.4a shows the adsorption isotherms at the temperature of25, 35and45◦C,and the Langmuir plots are displayed in Fig.4b.The adsorption capacity increases with increasing adsorption temper-ature,suggesting endothermic adsorption.The Gibbs free energy change G can be calculated by the fol-lowing Eq.(5)[5,6,10,35]:G=−RT ln b(5)(where R is the gas constant)The Langmuir constant b(dimension:L/mol)can be obtained from the slope/intercept of the Langmuir plot of Fig.4b.The negative free energy change( G)shown in Table2suggests spontaneous adsorption under the adsorption conditions.E.Haque et al./Journal of Hazardous Materials181 (2010) 535–542539Fig.4.(a)Adsorption isotherms for MO adsorption over PED-MIL-101at25,35and45◦C;and(b)Langmuir plots of the isotherms(a);(c)Adsorption isotherms for MO adsorption over MIL-101at25,35and45◦C;and(d)Langmuir plots of the isotherms(c).The enthalpy change H can be obtained by using the van’t Hoffequation[5,44]:ln b= SR− HRT(6)The calculated H,obtained from the(−slope×R)of the van’tHoff plot(Fig.5),is29.5kJ/mol,confirming endothermic adsorp-tion in accord with the increasing adsorption capacity associatedwith increasing adsorption temperature(Fig.4a).The endothermicTable1Textural properties,the pseudo-second-order kinetic constants(k2)with correlation constants(R2)at various MO concentrations and the maximum adsorption capacities (Q0)of thefive adsorbents.Adsorbent(pore size,nm)BET surfacearea(m2/g)Total porevolume(cm3/g)Pseudo-second-order kinetics constants k2(g/(mg min))Maximum adsorptioncapacity,Q o(mg/g) 30ppm40ppm50ppmk2R2k2R2k2R2Activated carbon(<1.0)10680.50 2.17×10−40.987 2.34×10−40.981 2.59×10−40.97811.2MIL-53(<1.0)14380.557.23×10−40.9997.70×10−40.9997.84×10−40.99957.9MIL-101(1.6,2.1)3873 1.709.01×10−40.9999.19×10−40.9969.29×10−40.998114ED-MIL-101(1.4,1.8)3491 1.37 1.06×10−30.998 1.19×10−30.999 1.27×10−30.999160PED-MIL-101(1.4,1.8)3296 1.18 2.75×10−3 1.00 2.95×10−3 1.00 3.04×10−30.999194Table2The maximum adsorption capacity and thermodynamic parameters of MO adsorption over PED-MIL-101and MIL-101at different temperatures.Adsorbent Temp.(◦C)Q o(mg/g) G(kJ/mol) H(kJ/mol) S(J/mol/K)PED-MIL-10125194−32.535219−34.529.520945241−36.6MIL-10125114−31.935121−33.1 4.0012045140−34.3540 E.Haque et al./Journal of Hazardous Materials 181 (2010) 535–542Table 3The equilibrium adsorbed amount (q e )and pseudo-second-order kinetic constant (k 2)of fresh and reused PED-MIL-101s and ED-MIL-101s (Temperature:25◦C,C i :50ppm).Adsorbent Items Fresh 1st reuse 2nd reuse PED-MIL-101q e (mg/g)187186181k 2(g/mg min) 3.04×10−3 1.87×10−3 1.18×10−3ED-MIL-101q e (mg/g)130127123k 2(g/mg min)1.27×10−31.07×10−37.62×10−4Fig.5.van’t Hoff plots to get the H and S of the MO adsorption over the MIL-101and PED-MIL-101.adsorption may be due to a stronger interaction between pre-adsorbed water and the adsorbent than the interaction between MO and the adsorbent.However,further work is necessary to clarify this suggestion.The entropy change S can be obtained from the (intercept ×R )of the vant’t Hoff plot (Fig.5),and the obtained entropy change S is 208J/(mol K).The positive S means the increased randomness with adsorption of MO probably because the number of desorbed water molecule islarger than that of the adsorbed MO molecule (MO is very bulky compared with water;therefore several water may be desorbed by adsorption of a MO molecule).Therefore,the driving force of MO adsorption (negative G )on PED-MIL-101is due to an entropy effect (large positive S )rather than an enthalpy change ( H is positive).Fig.6.Effect of pH of MO solution on the adsorbed amount of MO over activated carbon and PED-MIL-101(C i :50ppm,adsorption time:4h).The thermodynamic properties were also determined for the case of MIL-101using the adsorption isotherms (Fig.4c)and the Langmuir plots at different temperatures (Fig.4d).Generally,the isotherms and Langmuir plots are similar to those of PED-MIL-101(Fig.4a and b).However,it should be mentioned that the adsorbed amount of MO over PED-MIL-101is high at very low concentra-tion (especially at 45◦C),which is very helpful to remove MO even at a low concentration.The adsorption free energy,enthalpy and entropy change over MIL-101,obtained from Fig.4d and Fig.5,are displayed in Table 2.Similar to PED-MIL-101,the adsorption of MO over MIL-101is a spontaneous process (negative G ).However,the absolute value of H is very small for the case of MIL-101.This may be due to a physical adsorption of MO and little desorption of pre-adsorbed water.The small free energy change ( S )sup-ports this assumption (small number of desorbed water molecules).However,a more detailed study will be necessary to understand the difference between MIL-101and PED-MIL-101in terms of the adsorption enthalpy and entropy changes.3.3.Effect of pH and regeneration of MOFsThe adsorption of a dye usually highly depends on the pH of the dye solution [2,6].MO adsorption at various pH values was mea-sured after equilibration withPED-MIL-101and activated carbon.As shown in Fig.6,the adsorbed amounts decrease with increas-ing the pH of the MO solution,which is quite similar to previously reported results [2,6].The decreasing of adsorbed MO with increas-ing pH might be due to the fact that the concentration of positive charge of adsorbents is decreased with increasing pH.Scheme 2.E.Haque et al./Journal of Hazardous Materials181 (2010) 535–542541Fig.7.(a)Effect of contact time on the MO adsorption and(b)Pseudo-second-order plots to show the re-usability of the spent PED-MIL-101.Even though more detailed work is necessary to clearly under-stand the mechanism of MO adsorption on Cr-BDCs,the mechanism may be explained with electrostatic interaction between MO and adsorbents(as proposed in Scheme2).MO usually exists in the sulfate form;therefore,there will be a strong electrostatic inter-action with an adsorbent having a positive charge.The positive charge distribution increases in the order of MIL-101<ED-MIL-101<PED-MIL-101as suggested in Scheme2.On the other hand the positive charge of PED-MIL-101will be decreased with increasing the pH of the solution due to the deprotonation of the proto-nated adsorbent.Therefore,the increase of adsorption capacity and kinetic constant with modification(MIL-101<ED-MIL-101<PED-MIL-101)or increasing acidity may be explained with the increased positive charge of the adsorbent,especially PED-MIL-101in a low pH condition.A similar adsorption mechanism of anionic dyes via electrostatic interaction has been reported in the case of chitosan [44]and NH3+-MCM-41[4].Facile regeneration of an adsorbent is very important for commercial feasibility.The re-usability of spent adsorbent(PED-MIL-101)is shown in Fig.7a.Even though the adsorption kinetic constants(shown in Table3which are derived from Fig.7b) decrease noticeably with the cycle of adsorption,the amount of adsorbed MO does not decrease much,suggesting the applicabil-ity of Cr-BDCs in the adsorptive removal of anionic dye materials from waste water.Similar re-usability of ED-MIL-101has also been observed(Table3,Supporting Fig.3).4.ConclusionThe liquid-phase adsorption of MO over MOF-type materials has been studied to understand the characteristics of dye adsorption on these materials.The adsorption capacity and adsorption kinetic constant of MIL-101are greater than those of MIL-53,showing the importance of porosity and pore size for adsorption,which is sim-ilar to reported -101,after being modified to have a positive charge,can be efficiently used to remove MO via liquid-phase adsorption.Based on the rate constant(pseudo-second or pseudo-first-order kinetics for adsorption)and adsorption capac-ity,it can be suggested that there is a specific interaction like electrostatic interaction between MO and the adsorbent for rapid and high uptake of the dye.The adsorption of MO over PED-MIL-101 at various temperatures shows that the adsorption is spontaneous and endothermic and the randomness increases with the adsorp-tion of MO.The driving force of MO adsorption over PED-MIL-101 is mainly due to an entropy effect rather than an enthalpy change. From this study,it can be suggested that the MOF-type materials may be applied in the regenerable adsorptive removal of anionic dye materials from contaminated water.AcknowledgementsThis work was supported by the National Research Founda-tion of Korea(NRF)grant funded by the Korea Government(MEST) (2008-0055718,2009-0083696).Appendix A.Supplementary dataSupplementary data associated with this article can be found,in the online version,at doi:10.1016/j.jhazmat.2010.05.047. References[1]G.Crini,Non-conventional low-cost adsorbents for dye removal:a review,Bioresour.Technol.97(2006)1061–1085.[2]A.Mittal,A.Malviya,D.Kaur,J.Mittal,L.Kurup,Studies on the adsorptionkinetics and isotherms for the removal and recovery of Methyl Orange from wastewaters using waste materials,J.Hazard.Mater.148(2007)229–240. [3]S.Chen,J.Zhang,C.Zhang,Q.Yue,Y.Li,C.Li,Equilibrium and kinetic studies ofmethyl orange and methyl violet adsorption on activated carbon derived from Phragmites australis,Desalination252(2010)149–156.[4]Q.Qin,J.Ma,K.Liu,Adsorption of anionic dyes on ammonium-functionalizedMCM-41,J.Hazard.Mater.162(2009)133–139.[5]Z.-M.Ni,S.-J.Xia,L.-G.Wang,F.-F.Xing,G.-X.Pan,Treatment of methyl orangeby calcined layered double hydroxides in aqueous solution:adsorption prop-erty and kinetic studies,J.Colloid Interface Sci.316(2007)284–291.[6]K.P.Singh,D.Mohan,S.Sinha,G.S.Tondon,D.Gosh,Color Removal fromWastewater Using Low-Cost Activated Carbon Derived from Agricultural Waste Material,Ind.Eng.Chem.Res.42(2003)1965–1976.[7]A.Bhatnagar,E.Kumar,A.K.Minocha,B.-H.Jeon,H.Song,Y.-C.Seo,Removalof anionic dyes from water using Citrus limonum(lemon)peel:equilibrium studies and kinetic modeling,Sep.Sci.Technol.44(2009)316–334.[8]G.Annadurai,R.-S.Juang,D.-J.Lee,Use of cellulose-based wastes for adsorptionof dyes from aqueous solutions,J.Hazard.Mater.92(2002)263–274.[9]V.Rocher,J.-M.Siaugue,V.Cabuil,A.Bee,Removal of organic dyes by magneticalginate beads,Water Res.42(2008)1290–1298.[10]J.-H.Huang,K.-L.Huang,S.-Q.Liu,A.-T.Wang,C.Yan,Adsorption of rhodamineB and methyl orange on a hypercrosslinked polymeric adsorbent in aqueoussolution,Colloid Surf.A:Physicochem.Eng.Aspects330(2008)55–61. [11]A.Ayar,O.Gezici,M.Küc¸ükosmano˘g lu,Adsorptive removal of methyleneblue and methyl orange from aqueous media by carboxylated diaminoethane sporopollenin:on the usability of an aminocarboxilic acid functionality-bearing solid-stationary phase in column techniques,J.Hazard.Mater.146(2007) 186–193.[12]X.Luo,L.Jhang,High effective adsorption of organic dyes on magnetic cellulosebeads entrapping activated carbon,J.Hazard.Mater.171(2009)340–347. [13]G.Férey,Hybrid porous solids:past,present,future,Chem.Soc.Rev.37(2008)191–214.[14]S.Kitagawa,R.Kitaura,S.-I.Noro,Functional porous coordination polymers,Angew.Chem.Int.Ed.43(2004)2334–2375.[15]O.M.Yaghi,M.O’Keeffe,N.W.Ockwig,H.K.Chae,M.Eddaoudi,J.Kim,Reticularsynthesis and the design of new materials,Nature423(2003)705–714.。
考研英语阅读应具备的五大能力考研英语阅读应具备的五大能力【摘要】考研阅读的重要性不言而喻,不仅占分多,而且得分难。
接下来就来谈谈考研阅读需要具备五大能力,各位同学可做参考。
携手2016大纲解析人第一时间解大纲,点击免费报名。
单词能力其实非常多阅读题目,最终归结到底与单词相互关联。
经典的例子如:例1:2003年第一篇Wild Bill Donovan would have loved the Internet.The American spymaster who built the Office of Strategic Services in the World War II and later laid the roots for the CIA was fascinated with information.Donovan believed in using whatever tools came to hand in the “great game” of espionage- spying as a “profession.” These days the Net, which has already re-made such everyday pastimes as buying books and sending mail, is reshaping Donovan’s vocation as well.21. The emergence of the Net has ________.[A] received support from fans like Donovan[B] remolded the intelligence services[C] restored many common pastimes[D] revived spying as a profession【解析】这道题定位在最后一句,由于Bill Donovan的职业(vocation)就是情报服务,所以说到底本题考察了re-made是否能和restore同意替换,reshape是否能和remold同意替换。
对高热患者行安脑丸与对乙酰氨基酚的效果对比黄建生;黄文丽;曾昭笔【摘要】目的:探讨高热患者采取安脑丸与对乙酰氨基酚治疗的效果.方法:选择我社区服务中心接诊的高热患者160例进行研究,入组时间2015年8月~2017年5月,纳入对象愿意配合本研究,以随机数表法分为安脑丸组与对乙酰氨基酚组,每组80例.安脑丸组患者接受安脑丸治疗,对乙酰氨基酚组患者采取对乙酰氨基酚治疗,对两组患者用药前、用药0.5 h、用药1h、用药2h、用药4h时体温进行记录,评价两组退热效果,并随访1个月统计离热复发情况,统计学分析两组指标.结果:两组患者在用药前体温无差异(P>0.05),用药0.5 h与用药4h时体温也无差异(P>0.05),但用药1 h、用药2h时对乙酰氨基酚组体温显著低于安脑丸组(P<0.05);两组患者退热效果比较无差异(P>0.05);随访1个月,安脑丸组高热复发1例,而对乙酰氨基酚组高热复发12例,比较差异有统计学意义(P<0.05).结论:安脑丸与对乙酰氨基酚应用在高热患者中均可取得不错的退热效果,但对乙酰氨基酚起效更快,而安脑丸起效慢,作用更持久,不易反弹,二者各有优劣,临床可合理选择.【期刊名称】《实用中西医结合临床》【年(卷),期】2018(018)002【总页数】3页(P130-132)【关键词】高热;安脑丸;对乙酰氨基酚【作者】黄建生;黄文丽;曾昭笔【作者单位】广东省东莞市虎门镇社区卫生服务中心东莞 523907;广东省东莞市太平人民医院东莞 511761;广东省东莞市虎门镇社区卫生服务中心东莞 523907【正文语种】中文【中图分类】R971.1发热属于临床比较常见的症状,而小儿属于高发群体。
基层医院收治的因呼吸道感染所致发热患者较多,尤其是学龄前小儿对发热反应比较敏感,发热会导致患儿耗氧量与心输出量增多,从而加重病情[1]。
长时间发热会导致机体不同程度损伤,加上小儿中枢神经发育不完全,发热持续时间过长诱发高热后会导致惊厥,甚至诱发永久性神经损伤[2]。
收稿日期:2010-04-19。
收修改稿日期:2010-05-22。
国家自然科学基金(No.6076019),江苏省自然科学基金(No.BK2006195),NCET 资助项目。
*通讯联系人。
E -mail :**************.cn第一作者:薛露平,男,25岁,硕士研究生;研究方向:纳米材料。
微波固相剥离法制备功能化石墨烯及其电化学电容性能研究薛露平1郑明波2沈辰飞1吕洪岭1李念武1潘力佳2曹洁明*,1(1南京航空航天大学材料科学与技术学院纳米材料研究所,南京210016)(2南京大学微结构国家实验室电子科学与工程学院,南京210093)摘要:通过微波固相剥离氧化石墨制备了功能化石墨烯材料。
石墨烯的剥离,是由于微波加热过程中氧化石墨烯片上的官能团分解为CO 2和H 2O ,产生的压力超过了片层间的范德华力。
形貌表征显示了石墨烯的有效剥离和纳米孔结构的形成。
红外光谱分析结果表明微波剥离的功能化石墨烯仍然有少量的官能团残留。
N 2等温吸附-脱附测试结果表明样品具有高比表面积(412.9m 2·g -1)和大孔容(1.91cm 3·g -1)。
电化学测试结果表明功能化石墨烯具有良好的电化学电容行为和207.5F ·g -1的比电容。
关键词:功能化石墨烯;微波辐射;超级电容器;电化学测试中图分类号:O613.71文献标识码:A文章编号:1001-4861(2010)08-1375-07Preparation of Functionalized Graphene Sheets via Microwave -Assisted Solid -StateProcess and Their Electrochemical Capacitive BehaviorsXUE Lu -Ping 1ZHENG Ming -Bo 2SHEN Chen -Fei 1L 譈Hong -Ling 1LI Nian -Wu 1PAN Li -Jia 2CAO Jie -Ming *,1(1Nanomaterials Research Institute,College of Materials Science and Technology,Nanjing University of Aeronautics and Astronautics,Nanjing 210016)(2National Laboratory of Microstructures,School of Electronic Science and Engineering,Nanjing University,Nanjing 210093)Abstract:Functionalized graphene sheets were produced by microwave -induced exfoliation of graphene oxide.Exfoliation happens when the oxygen -containing groups decomposed into CO 2and H 2O by microwave -heat,thus yielding pressures that exceed the Van der Waals attraction between the layers.X -ray diffraction,FTIR,SEM,TEM and nitrogen adsorption -desorption were used to characterize the samples.Scanning electron microscopy images show that the sample possesses nanoporous structures.Fourier -transform infrared spectroscopy characterization proves the existence of a few functional groups on the surface of graphene sheets.The results of nitrogenadsorption -desorption analysis indicate that the sample has high BET surface area (412.9m 2·g -1)and large pore volume (1.91cm 3·g -1).The electrochemical tests show that the sample has good electrochemical capacitive behaviorand high specific capacitance values about 207.5F ·g -1in aqueous KOH.Key words:functionalized graphene sheets;microwave irradiation;supercapacitor;electrochemical measurementsGraphene,an entirely new class of carbon with two dimensional (2D)structure,was first reported by Andre Geim and Kostya Novoselov in 2004[1].Graphene hasattracted great interest because of the unique physical,chemical,and mechanical properties arising from its 2D form [2-4].Its special nanostructure holds great promise第26卷第8期2010年8月Vol .26No .81375-1381无机化学学报CHINESE JOURNAL OF INORGANIC CHEMISTRY第26卷无机化学学报for potential applications,such as energy-storage materials[5-7],composite materials[8-11],mechanical resonators[12-13],and transistors[13-17].However,it is a challenge to produce graphene on large scale. Micromechanical cleavage of graphite to obtain graphene sheets was first reported in2004[1],but this method is not amenable to large-scale production of graphene.Recently,several promising methods for mass production of graphene sheets have been reported[17-26]. Chemically converted graphene sheets were prepared by the chemical reduction of exfoliated graphene oxide (GO)with reducing agents[17-20].Stoller et al.prepared graphene sheets by means of suspending GO in water and chemical reducing with hydrazine[20].This kind of graphene has some great performances,such as good conductivity and good supercapacitive properties(the specific capacitance of the sample was about135F·g-1 at a discharge current of10mA in5.5mol·L-1KOH aqueous solution).Functionalized graphene sheets (FGS)were reported to be preparedvia high temperature expansion of GO or a low-temperature reduction under high vacuum[18-21].Malesevic et al.produced few-layer graphene via microwave plasma-enhanced chemical vapor deposition(MW-PECVD)[25].However,high temperature or long reduction time is required for most of the methods listed above.For instance,the chemical reduction to exfoliated GO with reducing agents provides a meaningful approach to produce large-scale graphene sheets[17-20],but in most chemical reduction methods heating to nearly100℃for several hours is necessary.As for the MW-PECVD method,heating substrates to700℃is required[22].Furthermore,the thermal exfoliation of GO usually requires high temperature(above1000℃)[21-22]or extreme exfoliation condition(vacuum)[24].Therefore,rapid exfoliation of GO under a mild condition is needed for the preparation of FGS in large quantity.Cote et al.produced graphene sheets by flash irradiation using GO as precursor[23]. Thermal exfoliation of graphite intercalation compounds was reported by Falcao et ing microwaves as a heat source[27].Microwave irradiation has also been used for the synthesis of graphene sheets in solvents[28-29]. Hassan et al.produced graphene sheets supporting metal nanocrystals in aqueous and organic media by microwave irradiation[28].The main advantage of microwave irradiation is heating the samples uniformly and rapidly compared with other conventional heating methods.Here,the thermal reduction of GO is studied using microwave irradiation as heat source.More recently,many studies on the supercapactive behavior of graphene materials have been reported[7,20,24,30].Vivekchand et al.prepared the graphene by three different methods[7].The highest specific capacitance value of the sample was about 117F·g-1in1mol·L-1H2SO4aqueous electrolyte.A low-temperature exfoliation approach to produce graphenes under high vacuum was reported by Lüet al[24].The specific capacitance value of the obtained graphene materials was up to264F·g-1in5.5mol·L-1 KOH aqueous solution without any post-treatments without any post-treatments.Wang et al.prepared the graphene materials via a gas-solid reduction process[30]. The maximum specific capacitance value of the sample was205F·g-1at energy density of28.5Wh·kg-1in a 30wt%KOH aqueous solution.In this work,we prepared FGS using GO as the precursor via an easy microwave induced solid-state process and investigated its electrochemical capacitive properties.The FGS sample possesses high BET surface area and large specific capacities in aqueous KOH(2mol·L-1)electrolyte.The microwave-induced exfoliation approach provides a promising approach for mass production of graphenes at low cost.Moreover,the FGS products show great potential applications in electrochemical energy storage.1Experimental section1.1Preparation of FGSGO was prepared from natural graphite powders (universal grade,99.985%)according to hummers method[31-32].Simply,natural graphite powders were washed by5%HCl twice,then filtered with distilled water,and dried at110℃.10g of washed graphite powder was added to cold(0℃)concentrated H2SO4 30g of KMnO4was added gradually with stirring and cooling,so that the temperature of the mixture was1376第8期薛露平等:微波固相剥离法制备功能化石墨烯及其电化学电容性能研究controlled at not higher than20℃.The mixture was stirred at35℃for30min,then460mL distilled water was added slowly to the reaction vessel to cause an increase in temperature to90℃and the mixture was continued to be stirred for15min.Finally, 1.4L distilled water and100mL30%H2O2solution were added.After the reaction,the solution was held at room temperature for24h.The solid product was separated by vacuum filtration,washed with5%HCl aqueous solution until sulfate could not be detected with BaCl2, then the reaction product was dried under vacuum at 50℃for48h.Small amounts of the dried GO were added into a porcelain dish,then,the porcelain dish was placed inside a household microwave oven (G8023CSK-K32450MHz,800W)and irradiated at full power for different time in range of30~240s.The obtained samples were denoted as FGS1(30s),FGS2(1 min),FGS3(2min),and FGS4(4min).1.2CharacterizationX-ray diffraction patterns were performed by a Bruker D8-advance diffractometer equipped with graphite monochromatized Cu Kα,radiation(λ=0.15405 nm).The morphology of FGS was observed by transmission electron microscopy(TEM)(JEOL JEM-2100)and scanning electron microscopy(SEM) (Gemini,LEO1530).Nitrogen adsorption-desorption was measured with a Micromeritics ASAP2010 instrument.Fourier transform infrared(FTIR) spectroscopy was performed with a Nicolet-670FTIR spectrometer using the KBr pellet method.1.3Electrochemical testsThe electrochemical performance of FGS was evaluated by cyclic voltammetry(CV),galvanostatic charge-discharge(GC),and electrochemical impedance spectroscopy(EIS),which were done in a three-electrode experimental setup using2mol·L-1KOH aqueous solution as the electrolyte.The prepared electrode was used as the working electrode.A platinum sheet and a saturated calomel electrode were used as counter and reference electrode,respectively. The working electrode was prepared as follows:80wt% FGS,15wt%acetylene black,and5wt% polytetrufluoroethylene were well mixed and pressed onto a nickel grid(1cm2),and flaked under10MPa after being dried at353K for12h.The electrode contained about5mg of FGS.The CV,GC,and EIS measurements were carried out on CHI660C electrochemical workstation at room temperature.The potential rang of CV and GC was determined between-1.0and-0.2V(vs.SCE).The GC measurement was carried out in current density range of1~10A·g-1.The impedance spectroscopy measurement was performed with a frequency range of100kHz~0.01Hz(amplitude of5mV at open circuit potential).2Results and discussion2.1Characterization of FGSSince GO is the oxidation production of pristine graphite,there are many functional groups on the surface of its carbon sheets,such as hydroxyl,carboxyl, and epoxyl groups.Fig.1shows XRD patterns of the parent graphite,GO,FGS1,and pared with the pristine graphite,the native graphite peak disappears,and the feature diffraction peak of GO appears at10.4°,corresponding to an interlayer spacing (d-spacing)of0.85nm,which indicates the complete oxidation of the starting graphite and most oxygen is bonded to the planar surface of graphite after the oxidization[33].After the microwave-heating treatment, the sharp peak around10°at the XRD patterns disappears,indicating that oxygen intercalated into the interlayer spacing of graphite is largely removed by microwave irradiation.In Fig.1,FGS samples display amorphous structure patterns.Fig.1XRD patterns of graphite,pristine GO,FGS1and FGS31377第26卷无机化学学报Fig.2shows the FTIR spectra of GO,FGS1,andFGS3.In addition to a broad band(3427cm-1)due to-OH groups[34],the characteristic peaks appear at1734,1624,1400,1228,and1050cm-1can be assigned tothe C=O,aromatic C=C,carboxy C-O,epoxy C-O,andC-O groups on the surface of the GO paredwith the pristine GO,the intensity of the peaks at1734and1624cm-1for FGS samples decrease,and thepeaks at1400and1050cm-1disappear,whichindicates that microwave irradiation removes most ofthe functional groups on the surface of the GO layersand still leaves a few residual functional groups on the surface of graphene sheets.Low-magnification scanning electron microscopy (SEM)image(Fig.3(a))of FGS3shows that the sample has many nanopores between the sheets,which results from the thermal exfoliation of GO.The nanoporous structure formed after the pressure generated by the decomposition of oxygen-containing groups via microwave-heat was enough to overcome the Van der Waals forces binding the GO sheets together.The high magnification SEM and transmission electron microscopy(TEM)images(Fig.3(b)and Fig.3(c))of FGS3show a wrinkled paper-like structure of the ultrathin graphene sheets and stacking of sheets.In Fig.3(d),the selected area electron diffraction shows only weak and diffuse rings,which indicates that the graphene sheets lose the long range ordering.Fig.2FTIR spectra of GO,FGS1,and FGS3Fig.3SEM images of FGS3(a,b),TEM and selected area electron diffraction pattern(SAED)of FGS3(c,d)The results of nitrogen adsorption-desorption analysis(Fig.4(a))also prove that the FGS samples have nanoporous structure.Fig.4(b)indicates that these samples have a broad pore size distribution from2to 200nm.The BET surface areas,pore volumes,and average pore sizes of the samples are shown in Table1. It can be found that,compared with FGS3(2min irradiation),the BET surface areas of FGS samples have no significant change after extending the processing time.Furthermore,the BET surface areas of FGS areFig.4(a)Nitrogen adsorption-desorption isotherms of FGS1and FGS3.(b)BJH pore size distributions from adsorption branches for FGS1and FGS31378第8期lower than the theoretical limit(2630m2·g-1)of graphene[23].It indicates that the FGS products contain extensive domains of stacked graphitic layers.2.2Electrochemical testingThe supercapacitive behavior of FGS3is analyzed using cyclic voltammetry(CV),galvanostatic charge-discharge(GC),and electrochemical impedance spectroscopy(EIS),which are done in a three-electrode system in aqueous KOH(2mol·L-1)electrolyte.Fig.5(a) shows the CV curves of FGS3with different scan rates (5~50mV·s-1).At a relatively low scanning rate,the CV curves of FGS3exhibit rectangular-like shape,even at a scanning rate as high as50mV·s-1,the CV curve still shows a rectangular shape with small distortion,indicating an excellent supercapacitive behavior.Discharge curves of the sample are performed at a current density range of1~10A·g-1.As seen in Fig.5 (b).The specific capacitance is evaluated from the slope of the discharge curves,according to the equation:C m= IΔt/(mΔv)[35],where I is the current of charge-discharge,Δt is the time of discharge,m is the mass of active materials in the working electrode,andΔV is0.8V. The evaluated results(Table2)indicate that FGS3 possesses higher capacitance retention(72.3%)at a current density of10A·g-1.Specific capacitance per surface unit C SA(μF·cm-2)is calculated using equation: C SA=C m/SA[36],where SA is the BET surface area(m2·g-1).The BET surface area of mesoporous carbon CMK-Table1BET surface areas,pore volumes,and average pore sizes of the FGS samples Sample BET surface area/(m2·g-1)Pore volume/(cm3·g-1)Average pore size/nmFGS1319.7 1.4117.6FGS2338.2 1.5318.1FGS3412.9 1.9118.5FGS4408.7 1.6716.3Fig.5(a)Cyclic voltammograms of the FGS3obtained at different scan rates.(b)Galvanostatic discharge curves of FGS3at different current density range from1to10A·g-1and mesoporous carbon CMK-3at a current density of1A·g-1.(c)Electrochemical impedance spectra measured from100kHz to0.01Hz of the FGS3and GO(amplitude of5mV at open circuit potential).Inset shows an enlarged scale.(d)Cycling performance of FGS3 (current density:1A·g-1).薛露平等:微波固相剥离法制备功能化石墨烯及其电化学电容性能研究1379第26卷无机化学学报Table 2Specific capacitances obtained from GC methods and capacitance retention for FGS33is around 1196m 2·g -1and the specific capacitance ofCMK -3at the current density of 1A ·g -1is about 124.4F ·g -1.The specific capacitance per surface areaof FGS3calculated is about 50.3μF ·cm -2at the currentdensity of 1A ·g -1,which is much higher than 10.4μF ·cm -2afforded by CMK -3.The impedance spectra consist of a semicircle in high -frequency range and a line inclined at a constant angle to the real axis in low -frequency range.The semicircle portion observed at high frequencies corresponds to the charge transfer limiting process.As we can see from Fig.5(c),low -down semicircles are observed at high frequency region,from the diameter of semicircle,the internal resistance of FGS3is lower than GO.It indicates that the conductive performance of FGS3is enhanced significantly.The inclined line in low -frequency range is attributed to Warburg impedance that is associated with electrolyte diffusion through the pared with GO,the imaginary part of the impedance spectra at low frequencies of FGS3is much closer to a 90°line in an ideal capacitor,indicating an ideal supercapacitive behavior of FGS3.Moreover,the electrical conductivity of FGS is an effective indicator to the exfoliation extent of GO [37].The results show the effective exfoliation of GO.Long cycle life of supercapacitor is important for its practical applications [38-39].Fig.4(d)shows the variation of specic capacitance for FGS3at a constantcurrent density of 1A ·g -1.As can be seen,the sample possesses high capacitance retention (92.2%)after 500cycles of testing.For the supercapacitive electrode materials,the efficient adsorption of electrolyte ions is crucial to generate high specific capacitance [40].The morphology characterization of FGS shows that the samples have a nanoporous structure~and low degree of agglomeration.Different from conventional carbon materials used for supercapacitor,the structure of FGS allows theelectrolyte ion to penetrate both the outer and inner region of the solids.Therefore,both sides of exfoliated graphene sheets could be exposed to the electrolyte and contribute to the capacitance.Furthermore,the residual functional groups on the surface of FGS may improve the hydrophilicity of electrode and afford the pseudocapacitance [41-42],thus enhancing the overall charge storage capability.3ConclusionIn summary,a n easy,high yield,green,and fast microwave -induced solid state approach to the synthesis of FGS is reported using GO as precursor.The results of electrochemical tests indicate that the FGS sample has good supercapacitive behavior and conductivity.The present method can be used to prepare graphene sheets in large scale.The produced graphenes are expected to be used for further application in electrochemical energy storage and electrocatalysis.References:[1]Novoselov K S,Geim A K,Morozov S V,et al.Science ,2004,306:666-669[2]Dikin D A,Stankovich S,Zimney E J,et al.Nature ,2007,448:457-460[3]Wang G X,Yang J,Park J,et al.J.Phys.Chem.C ,2008,112:8192-8195[4]HUANG Gui -Rong(黄桂荣),CHEN Jian(陈建).CarbonTechniques (Tansu Jishu ),2009,1(28):35-39[5]Novoselov K S,Jiang D,Schedin F,et al.Proc.Natl.Acad.Sci.U.S.A .,2005,102:10451-10453[6]Takamura T,Endo K,Fu L,et al.T.Eletrochim.Acta ,2007,53:1055-1061[7]Vivekchand S R C,Rout C S,Subrahmanyam K S,et al.J.Chem.Sci .,2008,120:9-13[8]Stankovich S,Dikin D A,Dommett G H B,et al.Nature ,2006,442:282-286[9]Watcharotone S,Dikin D A,Stankovich S,et al.Nano Lett.,2007,7:1888-1892Sample Capacitance retention /%FGS3207.5192.5180.1150.072.3C m /(F ·g -1)1A·g -15A ·g -14A ·g -110A ·g -11380第8期[10]ZHANG Xiao-Yan(张晓艳),LI Hao-Peng(李浩鹏),CUI Xiao-Li(崔晓莉).Chinese J.Inorg.Chem.(Wuji Huaxue Xuebao), 2009,25(11):1903-1907[11]Singh V K,Patra M K,Manoth M,et al.New Carbon Mater.(Xinxing Tan Cailiao),2009,24(2):147-152[12]Bunch J S,Van Der Zande A M,Verbridge S S,et 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Da-Zhi(王大志),LIANGJi(梁吉).Chinese J.Inorg.Chem.(Wuji Huaxue Xuebao), 2003,19(2):137-141[42]Du Q L,Zheng M B,Zhang L F,et al.Eletrochim.Acta,2010,55:3897-3903薛露平等:微波固相剥离法制备功能化石墨烯及其电化学电容性能研究1381。
临床医学英语词汇小编为大家整理临床医学英语词汇,希望对你有帮助哦! absolute refractory period 绝对不应期absorbed dose rate 吸收剂量率absorbed dose 吸收剂量absorption coefficient 吸收系数absorption of light 光的吸收absorption spectrum 吸收光谱absorption 吸收,吸收作用absorptive cell 吸收细胞absorptivity 吸收率abstinence syndrome 戒断症状acceptor site 受位accessory n. 副神经acentric fragment 无着丝点片段acentric ring 无着丝点环acetaminophen 醋氨酚acetone 丙酮acidophilia 嗜酸性acidophilic body 嗜酸小体acinus 腺泡acrosome reaction 顶体反应acrosome 顶体actin filament 肌动蛋白丝actin 肌动蛋白action potential 动作电位action 作用activation 激活,活化activator 激活蛋白,激活剂,活化物active immunization 主动免疫active oxygen 活性氧active reabsorption 主动重吸收active transport 主动运输,主动转运acute experiment 急性实验acute inflammation 急性炎症acute proliferative glomerulonephritis 急性增殖性肾小球肾炎acute radiation injury 急性放射损伤acute reaction 急性反应acute viral hepatitis 急性病毒性肝炎adaptation 适应addiction 成瘾性additional pressure 附加压强adenine (A) 腺嘌呤adenocarcinoma 腺癌adenoma 腺瘤adenosine 腺苷adenovirus 腺病毒adequate stimulus 适宜刺激adhering junction 粘合连接adhesion molecule 粘附分子adipose tissue 脂肪组织adjuvant 佐剂adoptive immunity 过继免疫adrenal gland 肾上腺adrenergic drug 肾上腺素药adrenergic receptor 肾上腺素受体adrenergic 肾上腺能的adrenoceptor blocking drug 肾上腺素受体阻断药adrenoceptor 肾上腺受体adrenocortical hormone 肾上腺皮质激素adrenomimetic drug 拟肾上腺素药adsorption 吸附adult 成人, 成年人aerobe 需氧菌aerobic dehydrogenase 需氧脱氢酶affinity maturation 亲和力成熟affinity 亲和力aflatoxin 黄曲霉毒素after effect 后遗效应afterload 后负荷afterload 后负荷afterpotential 后电位agent 药剂agglutination of erythrocyte 红细胞凝集agglutinin 凝集素agglutinogen 凝集原aggregation 聚集,聚集态aging 老化,老年agonist 激动剂, 兴奋剂,主动肌air embolism 空气栓塞airborne transmission 空气传播airway resistance 气道阻力alanine 丙氨酸albinism 白化病albumin 白蛋白,清蛋白aldosterone 醛固酮all trans 全反构象allantois 尿囊allelic exclusion 位基因排斥allergen 过敏原,变应原allergy 变态反应allopurinol 别嘌呤醇allosteric effect 别构(位)效应allosteric enzyme 变构酶,别位酶allosteric regulation 别构调节allotype 同种异型alteration 变质alterative inflammation 变质性炎症alternation of generations 世代交替alternative pathway 旁路途径, 替代途径alveolar capillary membrane 肺泡-毛细血管膜alveolar carcinoma 肺泡上皮癌alveolar dead space 肺泡死腔,肺泡无效腔alveolar duct 肺泡管alveolar fluid 肺泡液体alveolar sac 肺泡囊alveolar septum 肺泡隔alveoli 腺泡,肺泡amantadine 金刚烷胺amastigote 无鞭毛体amebic dysentery 阿米巴痢疾amine 胺amino acid 氨基酸aminoacyl site A位,氨酰基位aminoacyl site A位,氨酰基位aminoglycosides 氨基糖甙类amitriptyline 阿密替林amnion 羊膜amniotic fluid 羊水amoxicillin 羟氨苄青霉素(阿莫西林) amphotericin B 二性霉素Bampicillin 氨苄青霉素(阿比西林)amplitude 振幅amrinone 胺吡酮amyloid degeneration 淀粉样变性anabolism 同化作用,合成代谢anaerobe 厌氧菌anaesthetic ether 麻醉乙醚anal canal 肛管anal membrane 肛膜analgesia 镇痛analgesics 镇痛药analyzer 检偏器anaphylaxis 过敏反anaplasia 间变anatomic shunt 解剖短路anatomical dead space 解剖无效腔或死腔anatomy 解剖学androgen 雄激素anemic infarct 贫血性梗死anergy 失能aneuploid 非整倍体angiology 脉管学angiotensin converting 血管紧张素转换angiotensin 血管紧张素angular momentum 角动量angular quantum number 角量子数animal for research 实验用动物animal model of human disease 人类疾病动物模型anisodamine 山莨菪碱anisotropy 各向异性ankyrin 锚定蛋白annulate lamellae 环孔板anoxia 缺氧antagonist 拮抗剂anterior cerebral a. 大脑前动脉anterior horn 前角anterior limb bud 上肢芽anterior limiting lamina 前界(膜)层anterior neuropore 前神经孔anterior poliomyelitis 脊髓前角灰质炎anthrax 炭疽antiadrenergic drug 抗肾上腺素antianginal drug 抗心绞痛药antianxiety 抗焦虑antiasthmatic drug 抗喘药antibiotics 抗生素antibody 抗体anticarcinoma drug 抗肿瘤药anticholinergic drug 抗胆碱药anticholinesterase drug 抗胆碱酯酶药anticoagulant 抗凝血药anticoagulation 抗凝anticodon 反密码子anticonvulsive drug 抗惊厥药antidiabetic drug 抗糖尿病药antidiarrheal agent 止泻药antidiuresis 抗利尿antiepileptic drug 抗癫痫药antigen presentation 抗原呈递antigen processing 抗原处理antigen 抗原antigenic drift 抗原漂移,抗原转变antihypertensive drug 抗高血压药antiinflammatory agent 抗炎药antimalarial drug 抗疟药antimanic drug 抗躁狂药antituberculosis drug 抗结核药anuria 无尿anus 肛门aorta 主动脉aortic arch 主动脉,弓动脉aortic body 主动脉体apneustic breathing 长吸式呼吸apoptosis 程序性细胞死亡,凋落,凋亡appendicitis 阑尾炎arachnoid 蛛网膜arch of aorta 主动脉弓archipallium 原脑皮层arginine 精氨酸argyrophil fiber 嗜银纤维artemisinin 青蒿素arterial hyperemia 动脉性充血arterial pressure 动脉血压arterial pulse 动脉脉?arteriole 微动脉arteriolosclerosis 细动脉硬化arteriosclerotic heart disease 动脉硬化性心脏病arteriovenous shunt 动静脉短路artery 动脉arthropod 节肢动物articular capsule 关节囊artificial respiration 人工呼吸ascariasis 蛔虫病ascaris lumbricoides 似蚓蛔线虫ascorbic acid 抗坏血酸 (维生素C) asepsis 无菌asparagine 天冬酰胺aspartic acid 天冬氨酸aspirin 阿斯匹林assembly 组装associate neuron 联络神经元aster 星体astrocyte 星形胶质细胞asymmetric transcription 不对称转录asymmetry 不对称性atenolol 阿替洛尔atheroma 粥肿atherosclerosis 动脉粥样硬化atomic spectrum 原子光谱atrial septal defect 房间隔缺损atrial systole 心房收缩atrioventricular bundle 房室束atrioventricular bundle 房室束atrioventricular node 房室结atrium 心房atrophic gastritis 萎缩性胃炎atrophy 萎缩atropine 阿托品attenuated live vaccine 减毒活疫苗attenuator 衰减子atypia 异型性audition 听力auditory string 听弦auditory threshold 听阈auditory tube 咽鼓管auricle 耳廓auricle 耳廓autoclaving 高压蒸汽灭菌法autocrine 自分泌autoimmunity 自身免疫autoinfusion 自身输液autolysosome 自生性溶酶体automatic respiratory rhythm 自主呼吸节律automaticity 自律性autonomic nervous system 植物性神经系统,自主神经系autonomic thermoregulation 自主性体温调节autopsy 尸体解剖autoradiography 放射自显影术autoregulation 自身调节autotransfusion 自身输血axillary a. 腋动脉axillary n. 腋神经axolemma 轴膜axon 轴索,轴突axoplasm 轴浆,轴质azotemia 氮质血症bacillary dysentery 细菌性痢疾bacteremia 菌血症bacterial endocarditis 细菌性心内膜炎bacterial pneumonia 细菌性肺炎banding technique 分带技术barbiturates 巴比妥类baroreceptor reflex 压力感受性反射barrier system 屏障系统basal metabolism 基础代谢basal nuclei 基底核base pairing 碱基配对base 碱基basement membrane 基底膜,基膜basement membrane 基底膜,基膜basilic v. 贵要静脉basis pharmacology 基础药理学basophilia 嗜碱性behavioral thermoregulation 行为性体温调节benign tumor 良性肿瘤benzodiazepines 苯二氮biceps brachii m. 肱二头肌bidirectional propagation 双向传导biguanides 双胍类药物bile canaliculi 胆小管bile pigment 胆色素binary fission 二分裂法bioavailability 生物利用度biochemical pharmacology 生化药理学bioelectricity 生物电biological dosimeter 生物剂量仪biology 生物学biomembrane 生物膜biophysics 生物物理学biopsy 活组织检查bioscience 生命科学。
吸附热力学的英文English:Adsorption thermodynamics refers to the study of the heat effects involved in the process of adsorption, which is the accumulation of gas, liquid, or dissolved substances on the surface of a solid or a liquid. It encompasses the analysis of the energy changes, such as the heat of adsorption, enthalpy, and entropy, that occur during the adsorption process. The investigation of adsorption thermodynamics is crucial in understanding the physical and chemical properties of adsorbents and adsorbates, as well as in the design and optimization of adsorption processes in various industries. By studying the thermodynamics of adsorption, researchers and engineers can gain insights into the efficiency, selectivity, and performance of different adsorbents, ultimately leading to the development of more effective adsorption systems for environmental remediation, gas purification, and separation processes.中文翻译:吸附热力学指的是研究吸附过程中涉及的热效应,吸附是指气体、液体或溶解物质在固体或液体表面的积聚。
分析检测吸附条件对食用油中苯并(a)芘吸附脱除的影响张诗琪1,2,刘孟洁2,赵洲桥2,韩立娟1,2,3*,张维农1,2,3(1.大宗粮油精深加工教育部重点实验室,湖北武汉 430023;2.武汉轻工大学 食品科学与工程学院,湖北武汉 430023;3.湖北省油脂精细化工工程技术研究中心,湖北武汉 430023)摘 要:将醋酸纤维素负载在活性炭表面得到的改性活性炭应用于食用油中苯并(a)芘的吸附脱除,以吸附脱除率为衡量指标,从吸附剂用量、吸附温度和时间方面对吸附条件进行优化。
结果表明,在吸附剂添加量为油重的0.8%,110 ℃下吸附30 min的条件下,改性活性炭对苯并(a)芘的脱除率高达100%。
关键词:食用油;苯并(a)芘;吸附脱除Effect of Adsorption Conditions on the Adsorption and Removal of Benzo(a)pyrene in Edible OilZHANG Shiqi1,2, LIU Mengjie2, ZHAO Zhouqiao2, HAN Lijuan1,2,3*, ZHANG Weinong1,2,3(1.Key Laboratory for Deep Processing of Major Grain and Oil, Ministry of Education, Wuhan 430023, China;2.College of Food Science and Engineering, Wuhan Polytechnic University, Wuhan 430023, China;3.Hubei FineChemical Engineering Technology of Oil and Fat Research Center, Wuhan 430023, China) Abstract: Activated carbon modified with cellulose acetate loaded on the surface of activated carbon is applied to the adsorption and removal of benzo(a)pyrene in edible oil. The adsorption and removal rate is used as a measure, and the adsorption conditions are optimized from the amount of adsorbent, adsorption temperature, and time. The results showed that the optimal adsorption conditions were as follows: the amount of adsorbent added was 0.8% of the oil weight, and the removal rate of benzo(a)pyrene was as high as 100% after 30 minutes of adsorption at 110 ℃.Keywords: edible oil; benzo(a)pyrene; adsorption removal苯并芘为多环芳烃的代表性物质,根据其苯环的稠合位置可分为1,2-苯并芘、3,4-苯并芘、4,5-苯并芘等10多种物质,前两种有强致癌性,而4,5-苯并芘致癌作用较弱。
开启片剂完整性的窗户日本东芝公司,剑桥大学摘要:由日本东芝公司和剑桥大学合作成立的公司向《医药技术》解释了FDA支持的技术如何在不损坏片剂的情况下测定其完整性。
太赫脉冲成像的一个应用是检查肠溶制剂的完整性,以确保它们在到达肠溶之前不会溶解。
关键词:片剂完整性,太赫脉冲成像。
能够检测片剂的结构完整性和化学成分而无需将它们打碎的一种技术,已经通过了概念验证阶段,正在进行法规申请。
由英国私募Teraview公司研发并且以太赫光(介于无线电波和光波之间)为基础。
该成像技术为配方研发和质量控制中的湿溶出试验提供了一个更好的选择。
该技术还可以缩短新产品的研发时间,并且根据厂商的情况,随时间推移甚至可能发展成为一个用于制药生产线的实时片剂检测系统。
TPI技术通过发射太赫射线绘制出片剂和涂层厚度的三维差异图谱,在有结构或化学变化时太赫射线被反射回。
反射脉冲的时间延迟累加成该片剂的三维图像。
该系统使用太赫发射极,采用一个机器臂捡起片剂并且使其通过太赫光束,用一个扫描仪收集反射光并且建成三维图像(见图)。
技术研发太赫技术发源于二十世纪九十年代中期13本东芝公司位于英国的东芝欧洲研究中心,该中心与剑桥大学的物理学系有着密切的联系。
日本东芝公司当时正在研究新一代的半导体,研究的副产品是发现了这些半导体实际上是太赫光非常好的发射源和检测器。
二十世纪九十年代后期,日本东芝公司授权研究小组寻求该技术可能的应用,包括成像和化学传感光谱学,并与葛兰素史克和辉瑞以及其它公司建立了关系,以探讨其在制药业的应用。
虽然早期的结果表明该技术有前景,但日本东芝公司却不愿深入研究下去,原因是此应用与日本东芝公司在消费电子行业的任何业务兴趣都没有交叉。
这一决定的结果是研究中心的首席执行官DonArnone和剑桥桥大学物理学系的教授Michael Pepper先生于2001年成立了Teraview公司一作为研究中心的子公司。
TPI imaga 2000是第一个商品化太赫成像系统,该系统经优化用于成品片剂及其核心完整性和性能的无破坏检测。
Journal of Molecular Catalysis A:Chemical264(2007)153–161Preparation of mesoporous silica/polymer sulfonate composite materials Masahiro Fujiwara a,∗,Kumi Shiokawa a,Yingchun Zhu ba Kansai Center,National Institute of Advanced Industrial Science and Technology(AIST),1-8-31Midorigaoka,Ikeda,Osaka563-8577,Japanb Shanghai Institute of Ceramics,Chinese Academy of Sciences,Shanghai200050,People’s Republic of ChinaReceived21June2006;received in revised form22August2006;accepted9September2006Available online15September2006AbstractMesoporous silica/polymer sulfonate composite materials were prepared by simply mixing hexadecyltrimethylammonium bromide,polymer sulfonates and TEOS(tetraethoxysilane)in alkaline aqueous solution.Nafion and poly(sodium4-styrenesulfonate)were employed as polymer sulfonates.XRD patterns and nitrogen adsorption–desorption isotherms showed that the precipitates obtained had mesostructure similar to MCM-41.Especially,the crystallinity of hexagonal structure of composite materials synthesized with Nafion was high.From all the results obtained here, it is concluded that the polymer sulfonate resins might be incorporated in the wall framework of mesoporous silica matrix.However,when the excess amount of Nafion was mixed,the acid sites of Nafion were significantly lost in the obtained materials.These composite materials present new classes of organically modified mesoporous silicas,where organic polymers are incorporated in the framework of mesoporous silica.They were used as catalysts for␣-methylstyrene dimerization and Friedel–Crafts alkylation reaction of aromatics.©2006Elsevier B.V.All rights reserved.Keywords:Mesoporous silica;Nafion;Poly(styrenesulfonate);Nano-composite;Solid acid;␣-Methylstyrene dimerization1.IntroductionResearches on mesoporous silicas and related materials are importantfields of recent material science[1,2].Especially MCM-41and its analogues[2]are actively studied because of their high potentials for various applications.The function-alization of mesoporous silica with organic compounds began with the surface modification using silane compounds such as R-Si(OR )3[1,3].After this kind of approach,the framework modification using disilane compounds followed.These materi-als are often called periodic mesoporous organosilicas(PMOs) [4–6].For example,Inagaki and co-workers notified that ben-zene ring and analogues are completely incorporated into the framework of mesoporous silica materials,and that these mate-rials are effective acid catalysts after sulphonation[7].Another trend is the polymerizations in the pore voids of mesoporous materials:many researchers produced composite materials with the corresponding polymers by this method[8].Mesoporous composite materials,where an organic polymer is introduced into their“framework”,are also investigated.In2000,we briefly ∗Corresponding author.Tel.:+81727519253.E-mail address:m-fujiwara@aist.go.jp(M.Fujiwara).reported that Nafion resin,whose structure is illustrated inFig.1,was incorporated in the framework of M41S type ofmesoporous silica[9].This material was a unique catalyst for ␣-methylstyrene dimerization.Recently,another group devel-oped the composite materials with polyacrylate[10].In Fig.2,a classification of these composite materials of mesoporous sil-ica with organic components is proposed.Type(A)is surfacemodification using R-Si(OR )3compounds[1,3],and Type(B)isframework modification such as periodic mesoporous organosil-icas(PMOs)[4–7].Type(C)shows composite materials withpolymeric compounds in the pore voids[8].Composite meso-porous materials with polymers in the framework are namedType(D)here[9,10].In this paper,we wish to report further examination of thecomposite materials of mesoporous silica with Nafion resin.Thematrices of mesoporous materials are expected to offer orderednanostructures useful as solid support[11].Nafion resin is alsoa functional perfluorinated sulfonic acid polymer to be usedas acid catalyst[12]and as polymer electrolyte for fuel cellapplication[13].Composite materials of Nafion resin with amor-phous silica have been utilized in these technologies[14,15].The ordered nanostructures of Nafion and analogous resins withmesoporous silica matrix are expected to be useful for variousapplications.1381-1169/$–see front matter©2006Elsevier B.V.All rights reserved. doi:10.1016/j.molcata.2006.09.016154M.Fujiwara et al./Journal of Molecular Catalysis A:Chemical264(2007)153–161Fig.1.Structure of Nafion resin.2.Experimental2.1.Preparation of mesoporous silica/Nafion composite materialThe preparation procedure is considerably simplified from our previously reported method[9].Nafion solution commer-cial available was directly used and no hydrothermal treatment was performed.A typical synthesis of mesoporous silica/Nafion composite is following:5.0g of5%Nafion alcohol solution (from Aldrich)was added to200mL of the aqueous solution of NaOH(1.73g;43.25mmol)and hexadecyltrimethylammo-nium bromide(3.48g;9.55mmol),and this mixed solution was stirred for a few minutes.To this solution,16.69g(80mmol) of tetraethoxysilane(TEOS)was added dropwise for5min, and the resulting solution was further stirred for12h at room temperature.An as-synthesized sample thus obtained wasfil-tered,washed with sufficient amount of H2O and dried at80◦C for12h.Template was removed by refluxing with1M H2SO4 solution of EtOH(solid sample/EtOH solution=1g/150mL)for 12h.Thefiltered solid was refluxed again with pure EtOH(sam-ple/EtOH=1g/150mL)for12h,filtered,washed with H2O at room temperature and dried at80◦C for12h.2.2.Preparation of mesoporous silica/Nafion composite material from amorphous silica/Nafion compositeThe general preparation method of MCM-41type of meso-porous silica from porous amorphous silica is described in elsewhere[16].This procedure was applied to amorphous sil-ica/Nafion composite.The amorphous silica/Nafion composite used here was SAC-13purchased from Aldrich.To the aqueous solution of NaOH(0.15g;3.80mmol)with hexadecyltrimethy-lammonium bromide(0.37g;1.00mmol)in4mL of H2O,0.61g of SAC-13was added.After stirred for1h,the resulting mixture was placed in a stainless autoclave,sealed tightly and heated at 110◦C for24h under autogenous pressure.The following pro-cedures were similar to the above-mentioned process.2.3.Preparation of mesoporoussilica/poly(4-styrenesulfonate)composite materialTo the solution of NaOH(0.799g;19.98mmol)and hex-adecyltrimethylammonium bromide(1.582g;4.341mmol)in 90mL of H2O,0.412g of poly(sodium4-styrenesulfonate)dis-solved in10mL of H2O was added,and to this homogeneous solution8.403g(40.34mmol)of TEOS was mixed.The result-ing solution was stirred for2days at ambient temperature. The precipitate thus formed wasfiltered,washed with sufficient amount of H2O and air-dried.The following procedures were similar to the above-mentioned process.2.4.Preparation of mixture of Nafion with hexadecyltrimethylammonium bromideA5%alcohol solution of Nafion(7.656g;Nafion content: 0.353g;sulfonic acid equivalent:0.341mmol)was mixed with NaOH(0.038g:0.95mmol)in5mL of H2O.After removing solvent under reduced pressure,the residue was dissolved in a mixed solution of H2O(10mL)and EtOH(10mL).Finally hexadecyltrimethylammonium bromide(0.125g;0.343mmol) was added.After about1day,white precipitate obtained was filtered and air-dried.2.5.Preparation of mixture of poly(4-styrenesulfonate)with hexadecyltrimethylammonium bromideThe solution of0.412g of poly(sodium4-styrenesulfonate) in6mL of H2O was mixed with the aqueous solution(50mL)of hexadecyltrimethylammonium bromide(0.728g;2.00mmol). The white precipitate was formed in a few minutes.After stirring for1h,the white precipitate wasfiltered and dried at60◦C. 2.6.Product characterizationsXRD patterns were recorded with a MAC Science MXP3V diffraction apparatus with Nifiltered Cu K␣radiation (λ=0.15406nm).N2adsorption-desorption isotherms were obtained at−196◦C(in liquid N2)using a Bellsorp Mini instru-ment(BEL JAPAN Inc.).BJH calculation was performed toesti-Fig.2.Conceptual schemes of composite materials of mesoporous silica with organic components.M.Fujiwara et al./Journal of Molecular Catalysis A:Chemical264(2007)153–161155mate the mesopore size using adsorption branches of isotherms. Elemental analyses of silicon were performed by the alkali fusion-gravimetric method according to JIS G1212(Japanese industrial standard).Elemental analyses offluorine were car-ried out with the lanthanum-alizarin complexone method using a Shimadzu UV-1600photometry apparatus after the extraction of alkali fusion method.Elemental analyses of carbon were per-formed by the common combustion gas quantification method. Thermogravimetric analyses(TGA)were performed on a Shi-madzu TGA-50apparatus.All samples were held in a platinum sample holder and were heated under air from room temperature to800◦C at the rate of5◦C/min.FT-IR spectra were mea-sured on a Perkin-Elmer Spectrum One spectrometer.Transmit-tance electron microscope(TEM)images were obtained using a JEM-2100F(JEOL)high-resolution transmissionfield emis-sion electron microscope(HRTEM)operated at300kV.The acid capacities of composite materials were estimated by the titra-tion method.The composite materials were immersed in0.1M of aqueous solution of NaCl,and the acid amounts of the ion-exchanged solutions thus obtained were analyzed by titrating with0.01M NaOH using phenolphthalein as indicator.2.7.Catalytic reactionsThe experimental procedure of␣-methylstyrene(AMS) dimerization was described in our previous paper[9].A com-petitive Friedel–Crafts reaction of toluene and p-xylene with benzyl alcohol was performed by the mixed solution of toluene (0.92g,10mmol),p-xylene(1.05g,10mmol)and benzyl alco-hol(0.22g,2mmol)in the presence of a catalyst(0.05g)at 90◦C for7h with vigorous stirring.Afterfiltering the catalyst, thefiltrate was analyzed by a capillary GC.3.Results and discussion3.1.Synthesis of mesoporous silica/Nafion composite materialComposite materials made of mesoporous silica and Nafion resin were prepared by a procedure modified formesoporous Fig.3.XRD patterns of as-synthesized and template-free(solvent extracted) mesoporous silica/Nafion composite materials.(A)As-synthesized MCM/ Nafion-1.(B)As-synthesized MCM/Nafion-2.(C)Template-free MCM/Nafion-1.(D)Template-free MCM/Nafion-2.silica synthesis.TEOS was added to a homogeneous alkaline solution of hexadecyltrimethylammonium bromide with Nafion resin.After stirring at room temperature,as-synthesized com-posite materials of mesoporous silica and Nafion resin were obtained as a white precipitate.Although hydrothermal treat-ment in an autoclave was given in our previous paper[9],we found that this hydrothermal treatment is not essential for the synthesis after the publication of the paper.The surfactant as template was removed by refluxing in H2SO4–EtOH solution (1M of H2SO4).H2SO4is expected to contribute to both the regeneration of sulfonic acid sites in Nafion polymer resin and the surfactant removal.The sample names and the profiles of composite materials are summarized in Table1.The data of a composite material prepared under hydrothermal conditions[9] are also included in Table1as MCM/Nafion-H.Fig.3shows XRD patterns of two composite materials(MCM/Nafion-1andTable1Properties of various mesoporous silica/polymer composites materialsSample Starting ratio d100a SSA b(m2/g)PV c(cm3/g)PPD d(nm) g/mol e wt%f2θnmMCM/Nafion-1 3.13 5.21 2.32(2.34) 3.81(3.77)1239 1.12 2.52 MCM/Nafion-2 6.7211.18 2.20(2.22) 4.01(3.98)1211 1.26 2.75 MCM/Nafion-314.8724.76 2.20(2.28) 4.01(3.87)3330.26 2.52 MCM/Nafion-H g 6.5810.96 2.25(2.35) 3.92(3.76)918 1.00 2.75 MCM/PSS8.8815.19 2.14(2.24) 4.13(3.94)8380.66 2.75a d100:X-ray diffraction(100)interplanar spacing.In parentheses,as-synthesized sample.b BET specific surface area.c Primary mesopore volume calculated from adsorption branch of BJH pore size distribution curve.d Peak pore diameter from adsorption branch of BJH pore size distribution curve.e Starting ratio of polymer(as acid type)and TEOS;gram of polymer/molar of TEOS.f Estimated weight percentage when polymer is completely incorporated in solid material and all TEOS converts into silica(SiO2).g MCM/Nafion composite material we reported[9].156M.Fujiwara et al./Journal of Molecular Catalysis A:Chemical264(2007)153–161Fig.4.Infrared spectra of as-synthesized(A)and template-free(B)MCM/ Nafion-1composite material.MCM/Nafion-2)in as-synthesized and template-free forms. XRD patterns indicated the formation of the hexagonal structure characteristically observed in the MCM-41type of mesoporous silica[2].The peaks assigned to d110,d200and d210interpla-nar spacings were found besides those from d100interplanar ones in all four samples.The surfactants were removed success-fully by the extraction using H2SO4in EtOH with the hexagonal structure maintained.Template removal by calcination was not performed to avoid thermal decomposition of Nafion resin.The peaks derived from the hexagonally ordered structure became stronger after the template removal in both cases(MCM/Nafion-1and MCM/Nafion-2).Infrared spectra of as-synthesized and template-free (extracted)samples are shown in Fig.4.In the as-synthesized sample,strong absorptions of the surfactant were observed approximately at2929and2850cm−1(Fig.4A).These absorp-tions disappeared after the treatment with H2SO4(Fig.4B), indicating the complete removal of the surfactant.On the other hand,the absorptions of C–F stretching modes of Nafion resin at1210and1160cm−1were not found in either spectra,while they are detected in amorphous silica/Nafion composite[14a]. It seems that in the case of amorphous silica/Nafion compos-ite,the contact time of Nafion resin with alkaline solution is comparatively short(the preparation solution gels immediately), preventing the serious decomposition of C–F bonds[14a].In our case,Nafion resin was dissolved in the high alkaline solution for a long time,resulting in critical degradation.The TEM images of MCM/Nafion-1are shown in Fig.5.The ordered structure(hexagonally arranged)was confirmed from the layered lines in the solid.The distance between layers is estimated to be3.0–3.8nm,approximately according with that from XRD patterns.The nitrogen adsorption–desorption isotherms of the template-free samples are shown in Fig.6.Both samples, MCM/Nafion-1and MCM/Nafion-2,indicated the typical type IV isotherms(IUPAC)of ordered mesoporous silica materi-als.The pore size of MCM/Nafion-2was larger than that of MCM/Nafion-1.These results were consistent with the d100 interplanar spacings from XRD patterns(Fig.3).Specific sur-face areas(BET surface area)and pore volumes of both samples were over1000m2/g and1cm3/g,respectively.These data were at the level similar to the MCM-41type of mesoporous sil-icas[1,2],and considerably higher than those of amorphous silica/Nafion composite materials[15].These properties are similar to those of the sample prepared under hydrothermal con-ditions(MCM/Nafion-H)in our previous paper[9].Therefore, a simpler preparation method using the direct use of commer-cial reagent under ambient conditions proved to be applicable. However,when more than20wt%of Nafion resin was added to the starting solution,the ordered structure of the corresponding composite material was considerably collapsed(MCM/Nafion-3).The peak at2.28in2θobserved in the as-synthesized sample (Fig.7A)indicated its moderately ordered structure.However, this peak almost disappeared after the removal of template (Fig.7A),showing the destruction of the ordered structure. In Fig.7B,the nitrogen adsorption–desorption isotherm and the pore size distribution estimated from the BJH method of template-free MCM/Nafion-3are presented.The porosity of this sample was poor and the peak of the pore diameterwas Fig.5.TEM images of MCM/Nafion-1(template-free).M.Fujiwara et al./Journal of Molecular Catalysis A:Chemical264(2007)153–161157Fig.6.(A)Nitrogen adsorption–desorption isotherms of mesoporous silica/Nafion composite materials.( )Adsorption branch of MCM/Nafion-1;( )desorption branch of MCM/Nafion-1;( )adsorption branch of MCM/Nafion-2;(᭹)desorption branch of MCM/Nafion-2.(B)Pore size distributions estimated from the adsorption branches of the isotherms by BJH method.( )MCM/Nafion-1;( )MCM/Nafion-2.broad.The specific surface area and the pore volume decreased to333m2/g and0.259cm3/g,respectively.Thus,the addition of excess amount of Nafion resin inhibited the formation of ordered structure.Another approach to the preparation of the composite mate-rial was attempted by using an amorphous silica/Nafion com-posite.It is well known that porous amorphous silica can be transformed into mesoporous MCM-41type material in the pres-ence of surfactant in alkaline solution[2,16].An amorphous silica/Nafion composite material commercially available(SAC-13;Nafion content:approximately13wt%)was immersed in an alkaline solution dissolving hexadecyltrimethylammonium bromide.This solution system was placed in an autoclave to be hydrothermally treated by reacted at115◦C for24h[16]. The XRD patterns of as-synthesized and template-free samples thus obtained are shown in Fig.8.The crystallinity of the as-synthesized sample was poor,and after the removal of template the hexagonal structure nearly collapsed.Even in this case,a comparatively high content of Nafion resin(13wt%)is thought to prevent the formation of ordered structure in the case of MCM/Nafion-3.3.2.Analyses of composition of mesoporous silica/Nafion composite materialThe contents of Nafion resin in these composite materials were analyzed by various methods.The results of TGA measure-ment of these composite materials are listed in Table2.Nafion resin is thermally decomposed from150to600◦C[17],and the weight decrease of pure mesoporous silica(without Nafion resin)we prepared was measured4.78%due to the thermal dehydration of silanols in this temperature range.The corrected values of the weight decreases by this blank measurement are shown in the parentheses.Although there are no direct propor-tional relationships between the starting contents of Nafion and the weight decreases,combustible Nafion contents increased from MCM/Nafion-1to MCM/Nafion-3.A similar tendency was observed in the elemental analysis shown in Table2.The Fig.7.(A)XRD patterns of as-synthesized and template-free(solvent extracted)MCM/Nafion-3.(B)Nitrogen adsorption–desorption isotherm and the pore size distribution by BJH method from adsorption branch(in inset)of MCM/Nafion-3.158M.Fujiwara et al./Journal of Molecular Catalysis A:Chemical264(2007)153–161Fig.8.XRD patterns of as-synthesized(A)and template-free(B)mesoporous silica/Nafion composite material obtained from an amorphous silica/Nafion composite(SAC-13).carbon andfluorine contents increased with the starting Nafion resin contents.It should be noted that thefluorine contents were low in these composite materials,although the weight ratios of fluorine to carbon must be approximately3.2according to the chemical formula of Nafion(Fig.2)[14a].These lower con-tents offluorine indicated that carbon–fluorine bonds in Nafion resin were significantly cleaved during the preparation process, because aliphatic perfluoro group is known to be unstable under basic conditions(although aromatic C–F bond is reported to be tolerant in alkaline solution)[11a].No observation of C–F bonds in infrared spectra(Fig.4),which can be observed in amorphous silica/Nafion composite[14a],was likely to result from the decrease in thefluorine content in the resin.The acid capacities of these composite materials were estimated by the cation exchange method with NaCl[14].The acid equivalents are also summarized in Table2.The acid content of pure Si-MCM-41(with Nafion resin)was under 0.001mequiv.H+/g.Pure Nafion resin(NR-50)and its compos-ite material with amorphous silica(SAC-13;Nafion content: 13wt%)is reported to have0.89or0.14mequiv.H+/g of acid capacities,respectively[14].In the parentheses of Table2, the weight percentages of Nafion in the composite materials calculated from the measured acid capacities are listed on the assumption that all sulfonic acid sites of Nafion resin are active. The calculated Nafion content of MCM/Nafion-1(5.92wt%) from acid capacity was reasonably consistent with the estimated values from both starting ratio and TGA measurement.On the other hand,in the case of MCM/Nafion-2,the Nafion content estimated from the acid capacity(17.02wt%)was in discord with other results.Furthermore,the acid capacity of MCM/Nafion-3was approximately0.003mequiv.H+/g.From these results,it was concluded that high contents of Nafion in the composite materials led to the some decomposition of Nafion resin,while no significant changes were observed in the case of low Nafion contents.3.3.Synthesis of mesoporous silica/poly-sulfonate composite materialThe formation of composite materials of mesoporous silica with polyacrylate was recently claimed in a report[10],where a procedure analogous to ours was used.We also studied the prepa-ration of a composite material made of mesoporous silica and another poly-sulfonate.Poly(4-styrenesulfonic acid)sodium salt was employed for the synthesis.In a similar manner to Nafion, TEOS was added to the mixed alkaline solution of poly(sodium 4-styrenesulfonate)(PSS)and hexadecyltrimethylammonium bromide,forming a composite material(MCM/PSS)after stir-ring.The XRD patterns of the as-synthesized and template-free samples are shown in Fig.9A.Although the peak intensities of these two patterns were lower than those of composite materials with Nafion,an ordered structure in the nano-level was observed. In the as-synthesized MCM/PSS,peaks assigned to d110,d200 and d210interplanar spacings were found as well as d100inter-planar one.Those peaks are not so clear in the template-free MCM/PSS,and its pore structure might be a wormhole like one[18].The nitrogen adsorption–desorption isotherms of this MCM/PSS composite material presented in Fig.9B are basi-cally type IV.The peak pore diameter was found at2.75nm (in inset).Thus,a poly(styrenesulfonate)polymer can be suc-cessfully introduced into mesoporous silica material as well as Nafion resin.Table2Results of elemental analysis,TGA and acid capacity of mesoporous silica/polymer composite materialsSample Stating ratio(wt%)a Elemental analysis(wt%)b TGA(%)c Acid capacity(mequiv.H+/g)dC Si FMCM/Nafion-1 5.21 2.7539.1 1.659.06(4.27)0.0527(5.92)MCM/Nafion-211.18 2.8939.3 1.7110.75(5.97)0.1515(17.02)MCM/Nafion-324.76 3.9236.8 5.8713.99(9.21)0.003(0.3)a Starting weight composition of Nafion calculated from carbon in Nafion and silicon in TEOS,regarding as Nafion formula are n=7and m=1in Fig.1.b Elemental analyses of C,Si and F were performed by common combustion gas quantification method,alkali fusion-gravimetric method or lanthanum-alizarin complexone method,respectively.c Percentage of weight loss from150to600◦C.In parentheses,the corrected value by deducting the weight decrease(4.78%)by the dehydration of mesoporous silica prepared without Nafion is noted.d Acid capacity estimated from the titration of ion-exchanged solution from NaCl using NaOH solution.In parentheses,the weight percent of Nafion calculated from this acid capacity using the pure Nafion resin acid capacity[14a],0.89mequiv.H+/g(on the supposition that all sulfonic acid sites are active).M.Fujiwara et al./Journal of Molecular Catalysis A:Chemical 264(2007)153–161159Fig.9.(A)XRD patterns of as-synthesized and template-free (solvent extracted)mesoporous silica/poly(sodium 4-styrenesulfonate)composite material (MCM/PSS).(B)Nitrogen adsorption–desorption isotherm and the pore size distribution by BJH method from adsorption branch (in inset)of MCM/PSS.3.4.Mechanistic discussion on the formation ofmesoporous silica/poly-sulfonate composite materials It is well known that the polymer electrolyte such as ion-exchange resin and surfactant readily form their complex by their ionic interaction [19].When sodium polyacrylate or poly(4-styrenesulfonate)was mixed with hexadecyltrimethy-lammonium bromide in aqueous solution,their complexes were instantly produced as precipitates.On the other hand,sodium salt of Nafion resin obtained by neutralization with sodium hydroxide scarcely afforded the precipitate with the surfactant in aqueous solution.Only after the considerable evaporation of solvent,a white viscous solid was obtained.Fig.10shows XRD patterns of the complexes obtained from sodium salt of Nafion or sodium poly(4-styrenesulfonate)withhexadecyltrimethylam-Fig.10.XRD patterns of precipitated solids from Nafion resin (A)or sodium poly(4-styrenesulfonate)(B)with hexadecyltrimethylammonium bromide.monium bromide.In the XRD pattern of the complex from sodium poly(4-styrenesulfonate)and the surfactant,a sharp peak at 2.11in 2θ(interplanar space:4.18nm)was found (B in Fig.10).These kinds of XRD pattern often observed in the com-plexes of polyelectrolytes and surfactants indicate the formation of lamellar structure complexes of polymer electrolytes with sur-factants [19d].On the other hand,in the case of the complex from Nafion resin and surfactant,no clear peak was observed in the XRD pattern (A in Fig.10),indicating that Nafion forms no ordered complex with cationic surfactant.A broad peak found at 2.22in 2θ(interplanar space:3.98nm)is likely to be derived from the cluster structure of sulfonic acid parts of Nafion resin [20].This cluster structure might restrict the formation of the complex with surfactant.In Fig.11,a possible formation mechanism of composite material consisting of mesoporous silica and polymer sulfonate is displayed.Two routes of composite materials formation are assumed.In the case of MCM/PSS synthesis,some layered phases of poly(styrenesulfonate)and surfactant are formed at first.The hydrolysis of TEOS to silica occurs in this solu-tion.With the progress of the condensation of silanols (Si–OH)to siloxane bonds (Si–O–Si),the hexagonal structure by the influences of surfactant is formed gradually.However,the lay-ered structure of poly(styrenesulfonate)and surfactant is com-paratively strong so as to restrict the transformation of the layered structure to the hexagonal one (route A).The lower crystallinity of MCM/PSS is thought to be caused from this effect.On the other hand,complex compounds are scarcely formed from Nafion resin and surfactant,not suppressing the above-mentioned transformation and the fabrication of hexag-onal structure (route B).It is thought that the electrostatic interaction between the sulfonate group of Nafion and cationic surfactant compels the mixing of Nafion resin in aqueous phase as shown in route B of Fig.11,when the amount of Nafion is not overabound.It is not sure that Nafion resin bearing highly hydrophobic perfluoro main chain is incorporated into the aque-ous phase of the mixed solution.However,the low fluorine contents in MCM/Nafion composite materials confirmed by the160M.Fujiwara et al./Journal of Molecular Catalysis A:Chemical 264(2007)153–161Fig.11.Expected mechanisms of mesoporous silica/polymer sulfonate composite materials.elemental analysis suggested that the reaction of carbon–fluorine bond proceeds to eliminate fluorine in high alkaline solution.The main chains of Nafion resin become more hydrophilic by this reaction,increasing the affinity for silica matrix.Finally,the well-defined hexagonal structure of MCM/Nafion compos-ite materials is obtained in the case of low loading of Nafion resin.3.5.Catalytic Friedel–Crafts reaction by mesoporous silica/Nafion composite materialsWe have previously shown the unique behavior of meso-porous silica/Nafion composite materials for ␣-methylstyrene (AMS)dimerization.Representative results are listed in ing this catalyst,intermediate products (products 1and 2)are predominantly obtained and the further reaction (intramolecular Friedel–Crafts reaction)to form an indan deriva-tive (product 3)is inhibited,while the product 3was yielded effectively by amorphous silica/Nafion composite (SAC-13)[9].A competitive Friedel–Crafts type reaction of toluene and p -xylene with benzyl alcohol was examined using MCM/Nafion-1and SAC-13(Fig.12B).While no selectivity for the benzy-lation of toluene or p -xylene was observed in the reaction by SAC-13,the reaction of p -xylene occurred preferably in the case of MCM/Nafion-1catalyst.These results indicated that Friedel–Crafts reaction catalyzed by MCM/Nafion-1is more influenced by the substituents on the benzene ring than that by SAC-13.p -Xylene with two electron-donating groupsisFig.12.Results of ␣-methylstyrene (AMS)dimerization (A)and competitive Friedel–Crafts type reaction of toluene and p -xylene with benzyl alcohol (B).。
Living a healthy life is a journey that requires commitment and discipline. It involves making conscious decisions that impact our physical, mental, and emotional wellbeing. Here are some key aspects to consider when striving for a healthier lifestyle:1. Balanced Diet: Consuming a variety of foods is essential. This includes plenty of fruits and vegetables, whole grains, lean proteins, and healthy fats. Limiting processed foods, sugars, and salts can help maintain a healthy weight and reduce the risk of chronic diseases.2. Regular Exercise: Engaging in physical activity for at least 30 minutes a day can do wonders for your health. It not only helps in weight management but also improves cardiovascular health, strengthens muscles and bones, and boosts mood.3. Adequate Sleep: Getting enough sleep is crucial for the body to repair and rejuvenate. Adults typically need 79 hours of sleep per night. Good sleep hygiene, such as maintaining a consistent sleep schedule and creating a relaxing bedtime routine, can improve sleep quality.4. Stress Management: Chronic stress can have detrimental effects on health. Techniques such as meditation, yoga, deep breathing, and mindfulness can help manage stress levels. Its also important to find hobbies and activities that bring joy and relaxation.5. Hydration: Drinking enough water throughout the day is vital for maintaining body functions and promoting healthy skin. Aim for at least eight glasses of water daily, and more if youre physically active.6. Social Connections: Building and maintaining strong relationships with family and friends can contribute to emotional health and provide a support system during challenging times.7. Regular Checkups: Visiting healthcare professionals for regular checkups can help detect potential health issues early and ensure that any existing conditions are wellmanaged.8. Avoiding Harmful Behaviors: Refraining from smoking, excessive alcohol consumption, and drug use can significantly reduce the risk of various health problems.9. Lifelong Learning: Keeping the mind active through continuous learning can help prevent cognitive decline with age. This can be achieved through reading, taking up new hobbies, or learning new skills.10. Positive Attitude: Maintaining a positive outlook on life can improve mental health and overall wellbeing. Cultivating gratitude and focusing on the good aspects of life can contribute to a more positive attitude.Incorporating these elements into daily life can lead to a more fulfilling and healthier existence. Its important to remember that change is a gradual process, and consistency is key to forming lasting healthy habits.。
Safety is a paramount concern in our daily lives,and it is crucial to take proactive measures to ensure personal wellbeing.Here are some essential tips on how to keep safe:1.Awareness of Surroundings:Always be conscious of your environment.This includes being aware of traffic,people,and potential hazards in public spaces.2.Personal Protective Measures:Wear protective gear when necessary,such as helmets when cycling,reflective clothing when walking at night,and seatbelts when in a vehicle.3.Home Security:Secure your home with locks,alarms,and possibly security cameras. Make sure to lock doors and windows,even when you are at home.4.Online Safety:Be cautious with the information you share e strong,unique passwords for different accounts and be wary of phishing attempts and scams.5.Emergency Preparedness:Have a plan for emergencies,such as natural disasters or medical situations.This includes knowing the location of the nearest hospital,having a first aid kit,and being familiar with emergency procedures.6.Healthy Lifestyle:Maintain a healthy lifestyle to reduce the risk of illness and injury. This includes regular exercise,a balanced diet,and sufficient sleep.7.Avoiding Risky Behaviors:Refrain from engaging in activities that could put you in danger,such as drug use,excessive alcohol consumption,or reckless driving.8.Trusting Your Instincts:If something feels off or unsafe,trust your instincts and remove yourself from the situation if possible.9.Staying Informed:Keep uptodate with local news and advisories that could impact your safety,such as weather warnings or community alerts.munity Involvement:Engage with your local community to foster a sense of security.Knowing your neighbors and participating in neighborhood watch programs can contribute to a safer environment.11.Financial Safety:Protect your financial information by being cautious with transactions,especially online.Be aware of common financial scams and how to avoid them.12.Travel Safety:When traveling,research the safety of your destination,keep yourbelongings secure,and be mindful of local customs and laws.By integrating these practices into your routine,you can significantly reduce the risk of accidents and ensure a safer lifestyle.Remember,safety is a continuous process that requires vigilance and proactive measures.。
r 反应r class 反应类r correlation r相关r factor 推理因素r method r法r variable 反应变量rabbit 兔子rabies 狂犬病race 种族race attitude 种族态度race difference 种族差异race discrimination 种族歧视race diversity 种族差异性race prejudice 种族偏见race psychology 种族心理学race relation 种族关系racial difference 种族差别racial discrimination 种族歧视racial diversity 种族差异性racial identity 种族认同racial inheritance 种族遗传racial memory 种族记忆racial mixture 种族混合racial prejudice 种族偏见racial unconscious 种族潜意识racialism 种族主义racialist 种族主义者racism 种族歧视radar 雷达radial 半径radial method of rotation 半径轴转法radiance 光亮度radiant emittance 辐射发散度radiant flux 辐射束radiant heat method 热传导法radiant intensity 辐射强度radiant reflectance 辐射反射率radiantive heat transfer coefficient 辐射热传递系数radiate 辐射radiation 放射radiation genetics 放射遗传学radiation therapy 放射疗法radiation induced aberration 辐射诱导畸变radical behaviorism 激进行为主义radical idea 激进思想radical therapy 彻底治疗法radicalism 激进主义radio advertising 广播广告radioaction 放射性反应radioactive substance 放射物质radiobiology 放射生物学radiocardiogram 放射心电图radiocardiography 放射心电描记法radioelectrocardiogram 放射心电图radioelectrocardiograph 放射心电描记法放射心电描记法radioelectronics 无线电电子学radioelement 放射性元素radioencephalogram 放射脑电图radioencephalography 放射脑电描记法放射脑电描记法radiogenetics 辐射遗传学radioisotope 放射性同位素radiology 放射学radiolucent 射线可透过的radioman 无线电技师radiometer 辐射仪radiophobia 射线恐怖症radiophysics 放射物理学radiophysiology 放射生理学radioreaction 放射反应radioreceptor 放射性受体radiosensitive 对辐射敏感的radiosensitivity 辐射敏感性radiostimulation 辐射刺激作用radiosusceptibility 辐射易感性radiotherapeutics 放射疗法radiotherapy 放射疗法radiothermy 热放射疗法radium 镭radium therapy 放射疗法radius 半径rage 愤怒ragoni scina contrast 拉高尼西纳方形对比railroad nystagmus 铁道性眼振railroadphobia 恐火车症railway illusion 铁路错觉raleigh equation 拉雷方程raman shift 瑞曼移动rament 气质激素说rami cardiaci 迷走神经心支rami gastrici 迷走神经胃支ramification 分枝random 随机random access 随机存取random answer 随机回答random assignment 随机分派random assortment 随机分类random behavior 随机行为random case 随机情况random cause 随机原因random character 随机特征random choice 随机选择random difference 随机差random digit dialing 随机数字拨号random distribution 随机分布random disturbance 随机扰动random dot stereogram 随机点实体图random effect 随机效果random effect model 随机效果模式random enquire 随机询问random error 随机误差random event 随机事件random experiment 随机试验random factor 随机因素random fluctuation 随机变动random genetic drift 随机遗传漂变random group 随机组random group design 随机组设计random learning 随机学习random manner 随机状态random method 随机方法random model 随机模式random movement 随意动作random noise 不规则噪声random number 随机数random numbers 乱数表random numbers table 随机号码表random observation 随机观察random observational error 随机观测误差random occurrence 随机出现random order 随机顺序random pairs method 随机选对法random phenomenon 随机现象random reinforcement 随机强化random sample 随机样本random sampling 随机抽样random sampling error 随机抽样误差random sampling method 随机抽样法random searching 随机调查random selection 随机选择random shape 无意义图形random variable 随机变量random wave 无规波randomization 随机化randomization test 随机化检定randomized block 随机区组randomized block design 随机区组设计随机分组设计randomized experiment 随机化实验randomized groups design 随机组设计randomized response 随机反应randomness 随机性random access memory 随机存取random group design 随机分组设计random halves reliability 随机半分卷信度random tracking 随机跟踪range 全距range effect 值域效应range of activity 活动范围range of attention 注意广度range of audibility 听觉范围range of body movement 身体运动范围身体运动范围range of choice 选择范围range of discrimination 辩别域range of error 误差范围range of indeterminacy 不确定性范围range of observation 观察范围range of reaction 反应幅度rank 等级rank correlation 等级相关rank difference correlation 级差相关rank image 等级象rank image principle 等级象原理rank order 等级次序rank order correlation 等级次序相关rank order method 等序法rank test 等级检验ranked distribution 等级分布rankian therapy 郎氏治疗法ranking 等级评定ranking evaluation 排列评估ranking method 等级法rank sum test 等级总和检定ranschburg inhibition 郎斯伯格抑制ranvier s constriction 郎飞氏节ranvier s node 郎飞氏节rap 扣击rap group 研究小组raphe 中缝raphe nucleus 中缝核raphe system 中缝系统rapid change 速度改变rapid eye movement 快速眼动眼速动rapid eye movement sleep 快速眼动睡眠rapid reading 快速阅读rapid change theory 急剧变迁论rapid smoking treatment 猛吸戒烟法猛吸戒烟法rapport 感情融通rapport stage 融洽阶段rapprochement 和睦rapture 着迷rapturous 狂喜raptus melancholicus 忧郁发作ras 网状觉醒系统ras 网状激活系统rasch model 罗殊模型rat 大白鼠rate 率rate of audience 收听率rate of forgetting 遗忘率rate of growth 生长率rate of identity 知名率rate of increase 增长率rate of information transmission 信息传递率rate of population increase 人口增长率人口增长率rate of response 反应率rate of unemployment 失业率rate score 率数值rate test 速度测验ratee 受评者rater 估价人rater error 评审员误差rate limiting reaction 限度反应rating 评定rating error 评定误差rating method 评定法rating scale 评定量表rating scale method 等级量表法rating dating complex 追求富有对偶情结ratio 比率ratio aggregates 综合比率ratio analysis 比率分析ratio error 比率误差ratio estimation method 比值估计法ratio intelligence quotient 比率智商ratio iq 比率智商ratio measure 比率测量ratio of interest for home group 内群亲近率ratio of interest for outside groups 外群亲近率ratio reinforcement 比率强化ratio reinforcement schedule 比率强化方式ratio scale 比率量表ratio variable 比率变量ration of interest for home group 内群亲近率rational 有理的rational analysis 理性分析rational approach 推理研究法rational authority 理性权威rational behavior 理性行为rational behavior therapy 合理行为治疗rational characteristics of character 性格的理智特征rational choice 理性选择rational construction 合理建构法rational education 理性教育rational emotive therapy 理情治疗法rational emotive therapy groups 理情治疗团体rational feeling 理智感rational knowledge 理性认识rational learning 理解学习rational number 有理数rational psychology 理性心理学rational psychotherapy 理性心理治疗法理性心理治疗法rational science 理性科学rational social management 合理的社会管理rational task analysis 理性作业分析rational type 理性型rational validity 合理效度rational will 唯理意志rationale 理论根据rationalism 理性主义rationalistic method 推理法rationalists 唯理主义者rationality 理性rationalization 合理化rationalization 文饰作用rationalization of crime 犯罪合理化rationalization of management 管理合理化rationalization of operation 操作合理化操作合理化rational behavior therapy 理性行为治疗rational construct 合理建构法rational economic man 理性经济人rational emotive therapy 理性情绪治疗rational recall theory of learning 学习的理论回忆说rational theoretical model 推理理论模式推理理论模式raven advanced progressive matrices test 瑞文高级推理测验raven colored progressive matrices test 瑞文彩色推理测验raven progressive matrices 瑞文推理测验raven standard progressive matrices test 瑞文标准推理测验ravenous 贪食的raving 疯话raw data 原始资料raw deal 不公平待遇raw feel 直感raw observation 原始观察raw score 原始分数raw score method 原始分数法rbt (rational behavior therapy 理性行为治疗rcbf 区域性脑血流rcmr 区域性脑代谢率rcs 相对对比敏感度rda 阅读年龄rdq 阅读商数reach area 可达范围reach distance 可达距离reach envelope 可达包络线reach one s heart 自我反省reactance 对抗reactance theory 抗拒论reactant 反应物reacting substance 反应物质reaction 反应reaction center 反应中心reaction chain 反应链reaction formation 反向形成reaction hypothesis 反应假说reaction inhibition 反应抑制作用reaction key 反应键reaction latency 反应潜伏期reaction level 反应水平reaction method 反应法reaction norm 反应规范reaction of degeneration 变性反应reaction of flight 飞行反应reaction of flight 逃跑反应reaction pattern 反应模式reaction period 反应期reaction potency 反应潜能reaction potential 反应电位reaction psychology 反应心理学reaction range 反应范围reaction rate 反应速率reaction structure 反应结构reaction system 反应体系reaction threshold 反应阈reaction time 反应时间reaction time delay 反应时间延迟reaction time in old age 老年期的反应时间reaction time method 反应时法reaction time of action 动作反应时reaction to court decision 判决反应reaction to detention 拘禁反应reaction type 反应类型reaction velocity 反应速度reactional psychosis 反应性精神病reactionary 反动的reactionism 反动主义reactionist 反动分子reactivate 恢复活动reactive aggression 反应性攻击reactive behavior 反应性行为reactive depression 反应性抑郁症reactive disorder 反应性疾病reactive inhibition 反应性抑制反应性抑制reactive inhibition theory 反应性抑制说反应性抑制说reactive maladjusted disturbance 反应性适应障碍reactive need 反应性需求reactive psychosis 反应性精神病reactive schizophrenia 反应性精神分裂症reactive state 反应状态reactivity 反应性reactology 反应学reactor 反应者read aloud 朗读read back 复述read in 读入read only memory 只读存储器read out 读出readability 易读性readability of letter and numeral 字母数字易读性reader 读者readership 读者身份readership score 注目率readership survey 阅读率调查readiness 预备状态readiness for contest 争夺准备状态readiness grouping 预备性分组readiness program 准备程序readiness test 准备测验readiness to learn 学习准备reading 阅读reading ability 阅读能力reading achievement 阅读成就reading age 阅读年龄reading aloud 朗读reading comprehension 阅读理解reading disability 阅读无能reading disorder 阅读障碍reading efficiency 阅读效率reading grade 读书年级reading instruction 阅读教学reading interest 阅读兴趣reading ladder 阅读步骤reading level 阅读水平reading material 阅读材料reading measure 阅读测量reading mistake 阅读错误reading model 阅读模式reading psychology 阅读心理学reading quotient 阅读商数reading rate 阅读速度reading readiness 阅读准备reading skill 阅读技能reading span 阅读广度reading speed 阅读速度reading test 阅读测验readings 读物reading disabled child 阅读障碍儿童阅读障碍儿童reading free vocational interest inventory 非阅读性职业兴趣测验readout 读出readout 示值读数ready signal 准备信号reafference 再内导reafference 自传入感觉reafferent change 自传入感觉变化real anxiety 事实性焦虑real appearance 真象real behavior 真实行为real causes 真实原因real concept 真实的概念real goal 真实目标real judgment 真实判断real motion perception 真实运动知觉real movement 真动real movement perception 真动知觉real self 真实自我realism 现实主义realistic anxiety 现实性焦虑realistic consumers 现实主义消费者realistic thinking 现实性思维realistic writing and painting 写实reality 现实reality adaptation 现实适应reality anxiety 现实焦虑reality awareness 现实意识reality condition 现实性条件reality ego 现实我reality orientation 现实取向reality principle 现实原则reality sense 现实感reality testing 现实验证reality therapy 现实疗法reality therapy groups 现实治疗团体reality irreality 现实非现实reality principle 唯实原则reality testing 自我的现实判断realizability 可实现性realization 现实化really exist 确实存在realm 领域realm of spirit 精神领域realness 真实性reappraisal 重新评价rear 抚养rear view 后视rearing 抚养rearrange 重新安排rearrangement 重新组织rearrangement form test 重组式测验rearrangement test 重组测验reason 理由reasonable cognition 理性认识reasonable stage 理性阶段reasonableness 理性reasoned thinking 推理思维reasoning 推理reasoning test 推理测验rebellion 反抗行为rebelliousness 判逆性rebirth fantasy 再生幻想rebound 回跳rebound effect 回跳效应rebound phenomenon 复发现象rebus 画迷rebus writing 谜画写字recall 回忆recall bias 回忆偏误recall method 回忆法recall period 回忆期recall test 回忆测验recall type 回忆类型recall value 回忆价recapitulation 复述recapitulation theory 复演说recapitulation theory of play 游戏的复演说receive 接受receiver 接受者receiver operating characteristic curve 接受者操作特征曲线receiver operating curve 接受者操作曲线recency 近因recency effect 近因效应recent amnesia 近事遗忘recent period 近期recentering 再定中心reception learning 接受式学习reception of experience 经验的接受reception strategy 接受策略reception test 验收检查receptive 感受的receptive aphasia 感受型失语症receptive cell 感受细胞receptive character 接纳性格receptive dysphasia 接受型语言障碍receptive field 感受域receptive language 接受语言receptive neuron 感受神经元receptive orientation 依赖取向receptive style 被动接受型receptive field orientation 感受野定向receptivity 感受性receptor 感受器receptor 受体receptor cell 感受细胞receptor fibre 感受神经纤维receptor inhibitor 受体抑制物receptor potential 受纳器电位receptor site 受点recessive 隐性recessive character 隐性特征recessive gene 隐性基因recessive inheritance 隐性遗传recessive trait 隐性特质。
分子生物学名词解释大全AAbundance (mRNA 丰度):指每个细胞中mRNA 分子的数目。
Abundant mRNA(高丰度mRNA):由少量不同种类mRNA组成,每一种在细胞中出现大量拷贝。
Acceptor splicing site (受体剪切位点):内含子右末端和相邻外显子左末端的边界。
Acentric fragment(无着丝粒片段):(由打断产生的)染色体无着丝粒片段缺少中心粒,从而在细胞分化中被丢失。
Active site(活性位点):蛋白质上一个底物结合的有限区域。
Allele(等位基因):在染色体上占据给定位点基因的不同形式。
Allelic exclusion(等位基因排斥):形容在特殊淋巴细胞中只有一个等位基因来表达编码的免疫球蛋白质。
Allosteric control(别构调控):指蛋白质一个位点上的反应能够影响另一个位点活性的能力。
Alu-equivalent family(Alu 相当序列基因):哺乳动物基因组上一组序列,它们与人类Alu家族相关。
Alu family (Alu家族):人类基因组中一系列分散的相关序列,每个约300bp长。
每个成员其两端有Alu 切割位点(名字的由来)。
α-Amanitin(鹅膏覃碱):是来自毒蘑菇Amanita phalloides 二环八肽,能抑制真核RNA聚合酶,特别是聚合酶II 转录。
Amber codon (琥珀MM子):核苷酸三联体UAG,引起蛋白质合成终止的三个MM子之一。
Amber mutation (琥珀突变):指代表蛋白质中氨基酸MM子占据的位点上突变成琥珀MM子的任何DNA 改变。
Amber suppressors (琥珀抑制子):编码tRNA的基因突变使其反MM子被改变,从而能识别UAG MM子和之前的MM子。
Aminoacyl-tRNA (氨酰-tRNA):是携带氨基酸的转运RNA,共价连接位在氨基酸的NH2基团和tRNA 终止碱基的3¢或者2¢-OH 基团上。