Effects of Boron Purity, Mg Stoichiometry and Carbon Substitution on Properties of Polycrys

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氯氧镁改性与抗盐卤性能研究

氯氧镁改性与抗盐卤性能研究

氯氧镁改性与抗盐卤性能研究童义平1,林燕文2(1.韩山师范学院化学系,广东潮州 521041;2.韩山师范学院生物系,广东潮州 521041)摘 要: 文章研究了卤水对氯氧镁水泥性能的影响。

结果表明:氯氧镁水泥具有优良的抵抗中、高度卤水的能力( 20 Be !,15∀),但对低度卤水的抵抗能力则取决于所采用的抗水添加剂。

卤水对氯氧镁水泥性能的影响机理可能是由于其中的相5(5Mg (OH )2#MgCl 2#8H 2O)、相3(3Mg(OH)2#MgCl 2#8H 2O)、相2(2MgCO 3#Mg(OH)2#MgCl 2#6H 2O)在卤水中的溶解造成。

卤水浓度高时,溶解过程较小,抗卤水能力就强。

反之,溶解过程就大,抗卤水能力就差。

卤水浓度的变化就证实了这一点。

改性制得的氯氧镁水泥样品e #具有抵抗各种浓度卤水的能力。

关键词: 氯氧镁水泥;抗压强度;抗盐卤性能;改性中图分类号:O642.542 文献标识码:B 文章编号:1001-2214(2004)06-0020-03Studies on Improve ment Prope rtie s of Bittern Resistanceof Magnesium Oxychloride Ce mentTONG Yi ping 1,LIN Yan wen2(1.De pa rtme nt of C he mistry,Ha nshan No rma 1C olle ge,C ha ozhou Gua ngdo ng 521041,C hina;2.De pa rtme nt of Bi o lo gy,Ha nshan Nor mal College,C ha ozho u Gua ngdong 521041,China)Abstract: The influence of bi ttern on the property of magnesium oxychloride cement (Mg -ce ment)was studied.The resul t indicated much better bittern-resistance of Mg-cement in bittern higher than 20 Be !(15∀),and the ability of bittern-resistance of Mg-cement in bittern lower than 20 Be !(15∀)depending on the i mprovement wi th water-resistance additi ves.The influence of bittern on Mg-cement is perhaps due to the existent dissolution process of phase 5(5Mg(OH)2#MgCl 2#8H 2O),phase 3(3Mg(OH)2#MgCl 2#8H 2O)and phase 2(2MgCO 3#Mg (OH)2#MgCl 2#6H 2O)in bi ttern.The higher the concentration of bi ttern,the lower the degree of dissolution of phase 5,phase 3and phase 2,and the better the bi ttern-resis tance of Mg-cement;the lower the concentration,the higher the degree of dissolution,and the worse the bittern-resistance of Mg-cement.It was confirmed by the variation of concentration of bi ttern.The i mproved Mg-cement sample(e #)showed much better bi ttern-resistance in different con centration of bittern.Key words: magnesium oxychloride cement;compressive strength;bittern-resistance;improve ment收稿日期:2004-05-20作者简介:童义平(1965-),男,潮州人,博士,韩山师范学院化学系,副教授。

Effect of Surfactants on the Interfacial

Effect of Surfactants on the Interfacial

Effect of Surfactants on the Interfacial Tension and Emulsion Formation between Water and Carbon Dioxide Sandro R.P.da Rocha,Kristi L.Harrison,and Keith P.Johnston*Department of Chemical Engineering,University of Texas,Austin,Texas78712Received July8,1998.In Final Form:October7,1998 The lowering of the interfacial tension(γ)between water and carbon dioxide by various classes of surfactants is reported and used to interpret complementary measurements of the capacity,stability,and average drop size of water-in-CO2emulsions.γis lowered from∼20to∼2mN/m for the best poly(propylene oxide)-b-poly(ethylene oxide)-b-poly(propylene oxide)(PPO-b-PEO-b-PPO)and PEO-b-PPO-b-PEO Pluronic triblock copolymers,1.4mN/m for a poly(butylene oxide)-b-PEO copolymer,0.8mN/m for a perfluoropolyether (PFPE)ammonium carboxylate and0.2mN/m for PDMS24-g-EO22.The hydrophilic-CO2-philic balance (HCB)of the triblock Pluronic and PDMS-g-PEO-PPO surfactants is characterized by the CO2-to-water distribution coefficient and“V-shaped”plots of logγvs wt%EO.A minimum inγis observed for the optimum HCB.As the CO2-philicity of the surfactant tail is increased,the molecular weight of the hydrophilic segment increases for an optimum HCB.The stronger interactions on both sides of the interface lead to a lowerγ.Consequently,more water was emulsified for the PDMS-based copolymers than either the PPO-or PBO-based copolymers.IntroductionSupercritical fluid(SCF)carbon dioxide(T c)31°C,P c )73.8bar)is an environmentally benign alternative to organic solvents for waste minimization.It is nontoxic, nonflammable,and inexpensive.However,because of its very low dielectric constant, ,and polarizability per volume,R/v,CO2is a poor solvent for most nonvolatile lipophilic and hydrophilic solutes.1It may be considered a third type of condensed phase,different from lipophilic and hydrophilic phases.Consequently,it is possible to disperse either lipophilic or hydrophilic phases into CO2, in the form of microemulsions,emulsions,and latexes, given an appropriate surfactant.Because of the low values of and R/v for CO2,the most CO2-philic types of functional groups have low cohesive energy densities,e.g.,fluoro-carbons,fluoroethers,and siloxanes.2-6The solvent strength of carbon dioxide may be understood by the fact that the solubility of a polymer in carbon dioxide is highly correlated with the surface tension of the pure polymer melt.7For example,poly(fluoroacrylates)with low surface tensions of10-15mN/m are highly soluble,whereas poly-(dimethylsiloxanes)with surface tensions of20mN/m are moderately soluble,and hydrocarbon polymers with higher surface tensions show very low solubility.For nonpolar or slightly polar polymers,the surface tension is a measure of the van der Waals forces and is related to the cohesive energy density.Because R/v is so small for CO2,polymers with low cohesive densities and surface tensions are the most soluble.The first generation of research involving surfactants in SCFs addressed reverse micelles and water-in-SCF microemulsions,for fluids such as ethane and propane8,9 as reviewed recently.10,11Microemulsions are thermody-namically stable and optically transparent,with typical droplet diameters of about2-10nm.The mechanistic insight gained from these studies of phase equilibria, interfacial curvature,and droplet interactions in a su-percritical fluid is directly applicable to carbon dioxide. Attempts to form water-in-CO2(w/c)microemulsions have been elusive.6,12,13For PFPE COO-NH4+w/c microemul-sions,FTIR,UV-visible absorbance,fluorescence,and electron paramagnetic resonance(EPR)experiments have demonstrated the existence of an aqueous domain in CO2 with a polarity approaching that of bulk water,14as has also been shown by small-angle neutron scattering (SANS).15Organic-in-CO2microemulsions have also been formed for600molecular weight poly(ethylene glycol) (PEG600)and for polystyrene oligomers.16,17In many previous studies,surfactant activity in CO2has been characterized in terms of water uptake into a CO2 microemulsion.Since the results were negative most of the time,it has been difficult to determine how to design surfactants to the water-CO2interface.A more direct property,such as the interfacial tension,is needed to understand the activity of surfactants at various interfaces containing carbon dioxide.In SCF systems,only a few studies have measured the interfacial tension(γ)even for simple binary systems(1)O’Shea,K.;Kirmse,K.;Fox,M.A.;Johnston,K.P.J.Phys.Chem. 1991,95,7863.(2)McHugh,M.A.;Krukonis,V.J.Supercritical Fluid Extraction: Priciples and Practice,2nd ed.;Butterworth:Stonham,MA,1994.(3)Hoefling,T.A.;Newman,D.A.;Enick,R.M.;Beckman,E.J.J. Supercrit.Fluids1993,6,165-171.(4)Newman,D.A.;Hoefling,T.A.;Beitle,R.R.;Beckman,E.J.; Enick,R.M.J.Supercrit.Fluids1993,6,205-210.(5)DeSimone,J.M.;Guan,Z.;Elsbernd,C.S.Science1992,257, 945.(6)Harrison,K.;Goveas,J.;Johnston,K.P.;O’Rear,ngmuir 1994,10,3536.(7)O’Neill,M.L.;Cao,Q.;Fang,M.;Johnston,K.P.;Wilkinson,S. P.;Smith,C.D.;Kerschner,J.;Jureller,S.Ind.Chem.Eng.Res.1998, 37,3067-3079.(8)Fulton,J.L.;Smith,R.D.J.Phys.Chem.1988,92,2903-2907.(9)Johnston,K.P.;McFann,G.;Lemert,R.M.Am.Chem.Soc.Symp. Ser.1989,406,140-164.(10)Bartscherer,K.A.;Minier,M.;Renon,H.Fluid Phase Equilib. 1995,107,93-150.(11)McFann,G.J.;Johnston,K.P.In Microemulsions:Fundamental and Applied Aspects;Kumar,P.,Ed.;Dekker:New York,1998;Vol.in press.(12)Iezzi,A.;Enick,R.;Brady,J.Am.Chem.Soc.Symp.Ser.1989, No.406,122-139.(13)Consani,K.A.;Smith,R.D.J.Supercrit.Fluids1990,3,51-65.(14)Johnston,K.P.;Harrison,K.L.;Clarke,M.J.;Howdle,S.M.; Heitz,M.P.;Bright,F.V.;Carlier,C.;Randolph,T.W.Science1996, 271,624-626.(15)Zielinski,R.G.;Kline,S.R.;Kaler,E.W.;Rosov,ngmuir 1997,13,3934-3937.419Langmuir1999,15,419-428including carbon dioxide and a liquid phase.18-20None of these studies included a surfactant.Surfactants have been studied for the generation of CO2foams in water21typically for water-soluble surfactants.The effects of various surfactants on theγbetween supercritical CO2and PEG (600MW)were reported recently.16At276bar,the addition of1%PFPE COO-NH4+reducesγfrom3.2to2.1mN/m, and the interfacial area of the surfactant is437Å2/ molecule.Interfacial tension measurements have also been made between poly(2-ethylhexyl acrylate)(PEHA)and CO222and styrene oligomers and CO2.23As is well-known for water-in-oil(w/o)emulsions and microemulsions,the phase behavior,γ,and curvature are interrelated,as shown in Figure1.24A minimum inγis observed at the phase inversion point where the system is balanced with respect to the partitioning of the surfactant between the phases.25,26Upon change of any of the formulation variables away from this point,for example,the temperature or the hydrophilicity/hydro-phobicity ratio(in our case the hydrophilic/CO2-philic ratio),the surfactant will migrate toward one of the phases. This phase usually becomes the external phase,according to the Bancroft rule.27Unlike the case for conventional solvents,a small change in pressure or temperature can have a large influence on the density and thus on the solvent strength of a supercritical fluid.By“tuning”the interactions between the surfactant tail and the solvent,it becomes possible to manipulate the phase behavior,and therefore the activity of the surfactant at the interface and curvature,and also the extension of the surfactant tails.As an example of pressure tuning,a water-in-propane microemulsion is inverted to a propane-in-water microemulsion by varying the pressure by50bar in the C12EO6/brine/propane system, at constant temperature.28This system undergoes a phase inversion density,by analogy with the phase inversion temperature,for conventional systems.If the density is changed so that the surfactant prefers either phase over the other,the surfactant is less interfacially active and γincreases.16,22,23The objective of this study is to achieve a fundamental understanding of the lowering of the water-CO2inter-facial tension by different classes of surfactants and to use this knowledge to explain the formation and stability of water-in-CO2(w/c)emulsions.The surfactants include PFPE COO-NH4+,Pluronic R(PPO-b-PEO-b-PPO)and Pluronic L(PEO-b-PPO-b-PEO)triblock copolymers,poly-(butylene oxide-b-ethylene oxide)(PBO-b-PEO),and poly-(dimethylsiloxane)(PDMS)copolymers with PEO-PPO grafts(PDMS-g-PEO-PPO).Fromγmeasurements ver-sus concentration,the adsorption is investigated for PFPE COO-NH4+and used to determine the critical micro-emulsion concentration.For the PPO-and PDMS-based surfactants,the concept of a hydrophilic-CO2-philic bal-ance(HCB)is introduced by relatingγand the distribution coefficient of the surfactant to the EO fraction(see Figure 1).To understand howγand the HCB influence colloid stability,we chose to study w/c emulsions in contrast to previous studies of microemulsions,since so few of these surfactants form microemulsions.Emulsions are ther-modynamically unstable,but may be kinetically stable, with droplets from100nm to several micrometers in diameter.The presence of the surfactant at the interface lowers theγand thus the Laplace pressure,reducing the energy necessary to deform the interface.29The emulsions may be stabilized against flocculation due to van der Waals forces by steric stabilization,as has been analyzed theoretically,30-33and/or Marangoni stresses,due to gradients in interfacial tension at the interface.To characterize emulsion capacity,stability,and the average droplet size of the emulsions,an in-situ turbidity technique has been applied in addition to visual observations.The ability to design surfactants for the interface between CO2 and an aqueous phase based upon knowledge of the relationship between colloid formation and stability,phase behavior,andγis of interest for a wide variety of heterogeneous reactions and separation processes in CO2. Examples include dry cleaning,extraction with micro-(16)Harrison,K.L.;Johnston,K.P.;Sanchez,ngmuir1996, 12,2637-2644.(17)McClain,J.B.;Betts,D.E.;Canelas,D.A.;Samulski,E.T.; DeSimone,J.M.;Londono,J.D.;Cochran,H.D.;Wignall,G.D.;Chillura-Martino,D.;Triolo,R.Science1996,274,2049.(18)Heurer,G.Ph.D.Thesis,The University of Texas at Austin, 1957.(19)Chun,B.-S.;Wilkinson,G.T.Ind.Eng.Chem.Res.1995,34, 4371-4377.(20)Schiemann,H.;Wiedner,E.;Peter,S.J.Supercrit.Fluids1993, 6,181-189.(21)Lee,H.O.;Heller,J.P.;Hoefer,A.M.W.SPE Reservoir Eng. 1991,11,421-428.(22)O’Neill,M.;Yates,M.Z.;Harrison,K.L.;Johnston,P.K.;Canelas,D.A.;Betts,D.E.;DeSimone,J.M.;Wilkinson,S.P.Macromolecules1997,30,5050-5059.(23)Harrison,K.L.;da Rocha,S.R.P.;Yates,M.Z.;Johnston,K. P.;Canelas,D.;DeSimone,ngmuir1998,14,6855-6863.(24)Aveyard,R.;Binks,B.P.;Clark,S.;Fletcher,P.D.I.J.Chem. Technol.Biotechnol.1990,48,161-171.(25)Bourrel,M.;Schechter,R.S.Microemulsions and Related Systems:Formulation,Solvency and Physical Properties;Marcel(27)Ruckentein,ngmuir1996,12,6351-6353.(28)McFann,G.J.;Johnston,ngmuir1993,9,2942.(29)Walstra,P.Chem.Eng.Sci.1993,48,333-349.(30)Peck,D.G.;Johnston,K.P.Macromolecules1993,26,1537.(31)Meredith,J.C.;Johnston,K.P.Macromolecules1998,31,5507-5555.(32)Meredith,J.C.;Sanchez,I.C.;Johnston,K.P.;Pablo,J.J.d.Figure1.Schematic representation of phase behavior andinterfacial tension for mixtures of water,CO2,and nonionicsurfactants as a function of formulation variables.420Langmuir,Vol.15,No.2,1999da Rocha et al.emulsions and emulsions,phase transfer reactions,34,35and emulsion polymerization.36Experimental SectionMaterials.All of the surfactants were used as received,unless indicated.The CF 3O(CF 2CF(CF 3)O)∼3CF 2COO -NH 4+(PFPE COO -NH 4+),a gift from A.Chittofrati,37was stored in a desiccator.The single tail Krytox-sulfate,R -COOCH 2CH 2OSO 3--Na +,where R )CF 3(CF 2CF(CF 3)O)n CF 2CF 2-,and the triple tail Krytox-sorbitol surfactants were synthesized by E.Singley and Dr.E.J.Beckman at the University of Pittsburgh.38Pluronic L,PEO-b -PPO-b -PEO (PEO -PPO -PEO),and Pluronic R,PPO-b -PEO-b -PPO (PPO -PEO -PPO),surfactants were a gift from BASF.The block copolymer PEO-b -PBO (EO 15-BO 12,SAM185)(where the subscripts indicate the number of repeat units of each moiety)was provided by Pittsburgh Paint and Glass.The surfactant (CH 3)3SiO[Si(CH 3)2O]20[Si(CH 3)(R)]2OSi(CH 3)3,with graft R )(CH 2)3O(C 2H 4O)∼11H,(PDMS 24-g -EO 22),M w ∼2600,was a gift synthesized by Unilever.7SILWET L-7500(M w )3000),(CH 3)3SiO(Si(CH 3)2O)x (Si(CH 3)(R))y OSi(CH 3)3,with R )(CH 2)3O-(C 3H 6O)n Bu (PDMS 11-g -PO 39),with n ,x ,and y not specified,and SILWET L-7622(M w )10000),with a similar backbone,but R )(CH 2)3O(C 2H 4O)m Me (PDMS 105-g -EO 68),were provided by OSi Specialties,Inc.ABIL B 8851(M w ∼6000),(CH 3)3SiO(Si-(CH 3)2O)22(Si(CH 3)(R)O)4Si(CH 3)3,with R )(CH 2)3O(C 2H 4O)∼17-(C 3H 6O)∼4H (PDMS 28-g -EO 67-PO 17),and ABIL B 88184(M w ∼13000),(CH 3)3SiO(Si(CH 3)2O)73(Si(CH 3)(R)O)4Si(CH 3)3,with R ∼(CH 2)3O(C 2H 4O)∼32(C 3H 6O)∼7H (PDMS 79-g -EO 126-PO 28)were obtained from Goldschmidt AG.PDMS homopolymer with a M w of 13000was synthesized by J.M.DeSimone at U.N.Carolina.Poly(ethylene glycol)with a molecular weight of 600was obtained from Polysciences,Inc.Poly(butylene glycol)monoether,composed of an ethylene oxide backbone with an ethyl side group (PBO,800g/mol)was supplied by Air Products.Poly(propylene glycol)(1025g/mol)was obtained from Polysciences,Inc.,and used as received.Deionized water (NANOpureII;Barnstead)and instrument grade carbon dioxide (99.99%)were used for all experiments.Phase Behavior.Phase boundaries were determined in the variable-volume view cell as described in further detail else-where.7For a given weight of surfactant and CO 2,the pressure of the system was increased until a single phase was observed in the view cell.The pressure was then decreased slowly until the solution became slightly turbid.The pressure was then increased again,and the process was repeated.The pressure where the system became turbid was classified as the cloud point pressure.The pressure and temperature were measured to (0.2bar and (0.1°C,respectively.Interfacial Tension Measurements.The tandem variable-volume pendant drop tensiometer described previously 16was used to measure the interfacial tension between CO and water (γ).The apparatus consisted of two variable volume view cells (the drop phase cell and the measurement cell (continuous phase cell)),an optical rail for proper alignment,a light source,a video camera,and a computer.The drop phase cell contained water saturated with an excess amount of pure CO 2,and the continuous phase cell contained CO 2and surfactant (if present).In this configuration,the surfactant only has to diffuse short distances in the small volume of the droplet phase.Pendant drops were formed on the end of a stainless steel or PEEK capillary tube with an inside diameter ranging from 0.01to 0.03in.Once a suitable drop was formed,the six-port switching valve connecting the two cells was closed and timing of the drop age was started.Several images were recorded as a function of drop age.Images of the drop were obtained in a tagged imagefile format (TIFF)and the edge of the drop was extracted from data at various global threshold values using a C ++program.From the shape of the interface,the γmay be obtained from the Laplace equationwhere ∆P is the pressure differential across the interface,R 0is the radius of curvature at the apex of the drop,and z is the vertical distance from the apex.A set of three first-order differential equations was used to express Laplace’s equation,and a computer program 39,40was used to solve for γ.The density difference between the two phases was calculated by using an equation of state for pure CO 241and steam tables for pure water.The aqueous phase density was assumed to change less than 0.0025g/cm 3for the concentrations of surfactant studied.Emulsion Formation,Stability,and Average Droplet Size Estimation.Figure 2shows a schematic representation of the experimental apparatus,similar to a previous version,for turbidimetric measurement and visual observation of emulsion formation and stability.22The system consists of a 28-mL variable-volume view cell,an optical cell (0.1cm path length)which was mounted in a spectrophotometer (Cary 3E UV -vis),a high-pressure reciprocating pump (minipump with a flow rate of 8-80mL/min),and a manual pressure generator (High-Pressure Equip.,model 87-6-5).A six-port switching valve (Valco Instru-ments Co.,Inc.)with an external sampling loop was used to add water to the system.The pressure was monitored to (0.2bar with a strain gauge pressure transducer (Sensotec),and the temperature was controlled to within (0.1°C.Surfactant was initially loaded into the view cell,and the desired amount of CO 2was added with the pressure generator.The pressure was increased,and the system equilibrated at the desired T ,for ∼2h,by using a magnetic stir bar.The cloud point of the surfactant was obtained as described above.The solution was then recirculated,and deionized water was injected into the system via the 150-µL sample loop in the switching valve.The solution was sheared through a 130µm i.d.×50mm long stainless steel capillary tube upstream of the optical cell.Emulsion formation and stability were characterized based upon turbidity measurements versus time (t )at a constant wavelength (λ)650nm)and also visual observation.The turbidity is a measure of the reduction in transmitted intensity,τ)(1/l )ln(I 0/I ),where l is the path length and I 0and I are the incident and transmitted intensities,respectively.After the injection of each increment of water,the emulsion was stirred and recirculated for ∼20min (approximate time required for the absorbance to reach a maximum value).Immediately after recirculation and stirring were stopped,τmeasurements started.The stability was assessed from τas a function of t ,while the(34)Jacobson,G.B.;Lee,C.T.;daRocha,S.R.P.;Johnston,.Chem.,in press.(35)Jacobson,G.B.;Lee,C.T.;Johnston,.Chem.,in press.(36)Adamsky,F.A.;Beckman,E.J.Macromolecules 1994,27,312-314.(37)Chittofrati,A.;Lenti,D.;Sanguineti,A.;Visca,M.;Gambi,C.M.C.;Senatra,D.;Zhou,Z.Prog.Colloid Polym.Sci.1989,79,218-(39)Jennings,J.W.;Pallas,ngmuir 1988,4,959-967.Figure 2.Apparatus for emulsion formation and turbidimetry measurement.∆P )2γ/R 0+(∆F )gz(1)Surfactant Effect on Interfacial Tension Langmuir,Vol.15,No.2,1999421effective average droplet size was determined fromτversusλ.For a monodisperse system of nonabsorbing spheres in theabsence of multiple scatteringτis given byτ)3K*φ/2D,42where φis the dispersed phase volume fraction,D is the droplet diameter, and K*is the scattering coefficient.According to Mie theory,Κ*is a complex function of R(R∼D/λ,whereλis the wavelengthof the incident light)and m the ratio of the refractive indices ofthe dispersed and continuous phases.The refractive indices wereapproximated by those of the pure components,water(1.333)and CO2.43By evaluation of turbidities at two wavelengths,theaverage droplet size can be determined by an iteration proce-dure.44Results and DiscussionInterfacial Tension of the CO2-Water Binary System.The interfacial tension between pure CO2and water is shown in Figure3for two temperatures as a function of pressure,along with the data of Heurer18and Chun and Wilkinson.19Our interfacial tensions were measured1h after drop formation.Theγvalues obtained by Chun and Wilkinson19were measured with the capillary rise technique.Whereas local equilibrium was achieved within the capillary tube,the entire system was not at equilibrium.Heurer used the pendant drop technique; however,the values reported were obtained from the drop profile within10s of drop formation.Therefore,the lower values ofγin the present study suggest a closer approach to true equilibrium.A simple physical picture may be used to explain the behavior for most of the pressure range studied.16At pressures below70bar,γdecreases with increasing pressure.The cohesive energy density or free energy density of CO2is well below that of water at all pressures. The density and free energy density of CO2change over a wide range with pressure,whereas the values for essentially incompressible water are constant.As the density of the CO2phase increases,its free energy density becomes closer to that of water,andγdecreases.At low pressures where the density and free energy density change a great deal with pressure,the decrease inγis pronounced.At high pressures,where CO2is more “liquidlike”,it is much less compressible and the decrease inγwith pressure is small.For the CO2-PEG600interface,γwas predicted quantitatively with a gradientmodel and the lattice fluid equation of state.16The latticefluid model is less applicable for water due to thecomplexities resulting from hydrogen bonding and car-bonic acid formation.A cusp in the curve ofγversus pressure is observed attemperatures and pressures near the critical point of CO2.The region of the cusp inγshifts to slightly higherpressures as the temperature is increased above the criticaltemperature of CO2.For supercritical temperatures,themagnitude of the cusp increases as the temperature isdecreased toward the critical temperature.At25,1935,and38°C,the cusp in the interfacial tension is verynoticeable,while it becomes small at45°C and is notvisible at71°C.18The following argument explains how the cusp is relatedto the large compressibility of CO2.An upward pointingcusp has been observed for the surface excess of ethyleneon graphitized carbon black.45The excess adsorption canbe defined in terms of the density of the bulk phase andthe density of the interfacial region46where F(z)is the molar density of the fluid at a distancez from the surface.At pressures below the critical pressureregion,F(z)can be much larger than F,due to attractionof solvent to the surface,leading to a largeΓex.At higherpressures,the bulk fluid is much denser,so that thedifference between F(z)and F is much smaller resultingin a smallerΓex.As temperature increases above thecritical temperature of the solvent,the tendency of thesurface to raise F(z)to“liquidlike”densities diminishesandΓex decreases.Similar arguments apply to theadsorption of CO2at the water-CO2interface.TheenhancedΓex is manifested as the downward cusp inγ.Inboth examples,the cusps become broader and shift tohigher pressures at higher temperatures.Similar behavioris observed for peaks in plots of the isothermal compress-ibility of pure CO2versus pressure at constant temper-ature.To put the above results in perspective,new interfacialtension data are shown for the PEG600-CO2interface tocomplement earlier data16only at45°C(Figure4).Thevalues ofγfor the water-CO2interface are considerablylarger than those for the PEG600-CO2,PS(M n)1850),23CO2-PEHA(M n)32k)interfaces.22This result is dueprimarily to the much larger surface tension of water,∼72mN/m,versus that of PEG,∼35mN/m,and PEHA, 30mN/m.However,it is interesting thatγbetween CO2and water at high pressures,20mN/m,is below that forwater-hydrocarbon interfaces.For heptane and octane,the hydrocarbon-waterγis about50mN/m.This lower γis consistent with the higher miscibility between CO2 and water47versus hydrocarbons and water.The stronger interactions between CO2and water versus hydrocarbons and water are due to the small size of CO2which causes a smaller penalty in hydrophobic hydration,CO2’s quad-rupole moment,and,finally,Lewis and Bronsted acid-base interactions.Over the entire pressure range for PEG600-CO2at25and45°C,the interfacial tension decreased monotonicallywith increasing pressure,unlike the case for CO2-water(42)Yang,K.C.;Hogg,R.Anal.Chem.1979,51,758-763.(43)Burns,R.C.;Graham,C.;Weller,A.R.M.Mol.Phys.1986,59,(45)Findenegg,G.H.In Fundamentals of Adsorption;Myers,A.L., Belfort,G.,Eds.;Engineering Foundation:New York,1983;p207.Figure3.Interfacial tension at the CO2-water interface asa function of pressure at various temperatures.Γex≡∫(F(z)-F bulk)d z(2) 422Langmuir,Vol.15,No.2,1999da Rocha et al.at 35°C.The lack of a dip near the critical pressure may be due to the much lower compressibility at 25and 45°C versus 35°C.This contrast in behavior may also be due to a difference in the density gradient and thickness in the interfacial region for the two systems,for example,greater miscibility for the CO 2-PEG600system.Interfacial Tension:PFPE Ammonium Carboxy-late.The addition of small amounts of PFPE COO -NH 4+decreases γsubstantially as shown at 45°C and 276bar in Figure 5.As the concentration is raised above 0.03%surfactant,a discontinuity is observed,and the magnitude of the slope becomes much smaller.Because it has been shown that w/c microemulsions are formed in this system,14the discontinuity can be attributed to a critical microemulsion concentration (c µc)for the PFPE COO --NH 4+surfactant,as has been done for oil -water inter-faces.24At concentrations above the c µc,the less negative slope is caused by the addition of surfactant primarily to adsorption at the pendant drop interface,the change in γis reduced.The adsorption obtained from the Gibbs’adsorption equationfor the PFPE COO -NH 4+surfactant was 1.77×10-10mol/cm 2,which corresponds to a surface coverage of ∼100Å2/molecule.Such a high surface coverage is sufficient for the formation of microemulsions.A comparable value of ∼140Å2/molecule was measured by Eastoe et al.48at 500bar and 25°C for the hybrid hydrocarbon -fluorocarbon C 7F 15CH(OSO 3-Na +)C 7H 15surfactant in CO 2.This value was determined by assuming that all the surfactant is adsorbed at the interface of spherical droplets of 25Å2radius,as measured by SANS,with a polydispersity of ∼0.2.The substantial reduction in γand relatively high surfactant adsorption explain why it was possible to form a w/c microemulsion with PFPE COO -NH 4+.The same surfactant had an absorption of 400Å2/molecule at the CO 2-PEG interface.16Phase behavior studies indicated that PEG-in-CO 2microemulsions are also formed with this surfactant,but the nature of the core has not been characterized.16Interfacial Tension:Fluoroether Sulfate and Sorbitol Surfactant.The phase behavior of fluoroether sulfates and fluoroether sorbitols was measured by Singley et al.38for various molecular weights of single-,twin-,and triple-tailed surfactants.The surfactants were soluble in CO 2at 33°C and moderate pressure (<300bar).The sorbitol surfactants were found to be more soluble in CO 2than the sulfate ones,as expected due to the low solubilities of ions in CO 2,because of its low dielectric constant.The results showed that branching depresses the cloud point curve of a surfactant until the solubility becomes domi-nated by the overall molecular weight.These surfactants were used to form CO 2-in-water and middle-phase emul-sions with excess CO 2and water.38The interfacial tension was measured at the water -CO 2interface for the single-tailed M w 2500sulfate and the triple-tailed (7500g/mol total)sorbitol surfactants.Our measured cloud point for the 1.4%(w/w)CO 2sorbitol surfactant was 215.6bar at 45°C.For 0.56%sulfate surfactant,it was 139.8bar at 45°C.The sulfate surfactant did not lower the interfacial tension significantly over the pressure range of 180-283bar 45°C at a concentration of 0.56%.The interfacial tension was difficult to determine accurately,because bubbles and possibly surfactant precipitate appeared on the surface of the pendant drop within 15min of drop formation.The interfacial tension was estimated to be ∼15mN/m by using manual edge detection of the pendant drop.For the sorbitol surfactant,the interfacial tension decreased to ∼5.5mN/m at 276bar and 45°C with a concentration of 1.4%.Relative to other surfactants reported in this study,these surfactants were less successful in lowering the interfacial tension.Interfacial Tension:PPO -PEO -PPO,PEO -PPO -PEO,and PBO -PEO Surfactants.Block co-polymers containing CO 2-philic and hydrophilic (CO 2-phobic)functional groups may be designed to be active at the CO 2-water interface.In this section,the CO 2-philic blocks are poly(propylene oxide)and poly(butylene oxide),while the CO 2-phobic block is poly(ethylene oxide).TheFigure 4.Interfacial tension for the PEG600-CO 2interface at varioustemperatures.Figure 5.Interfacial tension for the water -CO 2-PFPE COO -NH 4+system at 45°C and 276bar.The dotted line is used to determine the surfactant adsorption via the Gibbs adsorption equation.A discontinuity is present at the critical micromemulsion concentration.Γ2)-1RT (d γd ln c 2)T ,P(3)Surfactant Effect on Interfacial Tension Langmuir,Vol.15,No.2,1999423。

沙利度胺的传说

沙利度胺的传说

The International Journal of Biochemistry&Cell Biology39(2007)1489–1499ReviewThe thalidomide sagaMagda Melchert a,∗,Alan List ba Moffitt Cancer Center and Research Institute,12902Magnolia Drive,SRB-4,Tampa,FL33612,USAb12902Magnolia Drive,SRB-4,Tampa,FL33612,USAAvailable online30January2007AbstractOver the past50years,thalidomide has been a target of active investigation in both malignant and inflammatory conditions. Although initially developed for its sedative properties,decades of investigation have identified a multitude of biological effects that led to its classification as an immunomodulatory drug(IMiD).In addition to suppression of tumor necrosis factor-alpha(TNF-␣), thalidomide effects the generation and elaboration of a cascade of pro-inflammatory cytokines that activate cytotoxic T-cells even in the absence of co-stimulatory signals.Furthermore,vascular endothelial growth factor(VEGF)and betafibroblast growth factor (bFGF)secretion and cellular response are suppressed by thalidomide,thus antagonizing neoangiogenesis and altering the bone marrow stromal microenvironment in hematologic malignancies.The thalidomide analogs,lenalidomide(CC-5013;Revlimid)and CC-4047(Actimid),have enhanced potency as inhibitors of TNF-␣and other inflammatory cytokines,as well as greater capacity to promote T-cell activation and suppress angiogenesis.Both thalidomide and lenalidomide are effective in the treatment of multiple myeloma and myelodysplastic syndromes for which the Food and Drug Administration granted recent approval.Nonetheless,each of these IMiDs remains the subject of active investigation in solid tumors,hematologic malignancies,and other inflammatory conditions.This review will explore the pharmacokinetic and biologic effects of thalidomide and its progeny compounds.©2007Elsevier Ltd.All rights reserved.Keywords:Thalidomide;Immunomodulatory agent;Angiogenesis;Lenalidomide;CC-4047Contents1.Introduction (1490)2.Pharmacokinetic properties (1490)3.Pharmacodynamic effects (1491)3.1.Immunomodulation (1491)3.2.T-cell activation (1492)3.3.Angiogenesis (1492)3.4.Bone marrow microenvironment (1493)3.5.Anti-tumor and apoptotic mechanisms (1493)4.Role of IMiDs in cancer therapy (1493)4.1.Multiple myeloma (1493)4.2.Myelodysplastic syndromes (1493)5.Conclusion (1496)References (1496)∗Corresponding author.Tel.:+18137453163;fax:+18137453071.E-mail addresses:Melcheme@moffi(M.Melchert),ListAF@moffi(A.List).1357-2725/$–see front matter©2007Elsevier Ltd.All rights reserved.doi:10.1016/j.biocel.2007.01.0221490M.Melchert,A.List/The International Journal of Biochemistry&Cell Biology39(2007)1489–14991.IntroductionThalidomide(Thalomid TM,Celgene Corp,Warren, NJ)is a synthetic glutamic acid derivative which was ini-tially developed in the early1950s as an anticonvulsant for the treatment of epilepsy.Following a lack of suffi-cient efficacy as an anti-epileptic,it was eventually mar-keted as a sleep aid and was also widely used as an anti-emetic during pregnancy(Randall,1990).Prior to its use in gravid women,the teratogenic effects of thalidomide in animals or humans were unknown.However,by1962, two published reports by William McBride in Australia and Widukind Lenz in Germany emerged describing limb and bowel malformations in children born to moth-ers who were exposed to thalidomide during pregnancy (Lenz,1962;McBride,1961).Use of this agent dur-ing thefirst trimester of gestation led to alarming rates of phocomelia,defects in long bones,absence of auri-cles,cleft lip,and cardiac and gastrointestinal anomalies. While thalidomide had not received approval by the Food and Drug Administration(FDA)in the United States (US)at this time due to concerns of neurotoxicity,the widespread international use of this drug as a sedative was eventually halted during the early1960s.The pharmacological effects of thalidomide extended beyond its neurosedative effects,and for that reason, it was subsequently investigated in a number of der-matologic,rheumatologic,and malignant diseases.In 1965,thefirst report of clinical activity in erythema nodosum leprosum(ENL)was serendipitously discov-ered by a dermatologist from Israel,Jacob Sheskin (Sheskin,1965).Thalidomide was found to be effec-tive in reducing fevers,night sweats,and improving skin lesions in a patient with ENL.However,it was not until1998that thalidomidefirst received approval by the FDA for the treatment of ENL(Pearson&Vedagiri, 1969;Sheskin,1965;Waters,1971).More recently, thalidomide was approved for the treatment of multi-ple myeloma in May2006,and has reported efficacy in a wide spectrum of malignant and non-malignant dis-eases.Access to this agent in the US is restricted,and requires participation in the System for Thalidomide Education and Prescription Safety(STEPS)program to prevent adverse outcomes related to teratogenicity (Zeldis,Williams,Thomas,&Elsaved,1999).Thalidomide and its analogs are immunomodula-tory drugs(IMiDs)that exhibit a multitude of biologic effects on cytokine and cell-mediated responses.These effects are largely responsible for the clinical efficacy seen in conditions such as lupus erythematosis,apt-hous ulcers that occur in human immunodeficiency virus and Behcet’s disease,ENL,graft versus host dis-ease,and cancer(Hamuryudan et al.,1998;Jacobson et al.,1997;Kumar,Witzig,&Rajkumar,2004;Parker et al.,1995;Pearson&Vedagiri,1969).Thalidomide is the most widely studied of the IMiDs;however, the newer structural analogs,CC-5013(lenalidomide, Revlimid TM,Celgene Corp.,Warren,NJ)and CC-4047 (Actimid TM),promise even greater activity for clinical development.These two analogs of thalidomide were developed in the mid-1990s with enhanced potency and a relatively favorable toxicity profile.This review will summarize the pharmacokinetic and biologic properties of thalidomide and its derivatives.2.Pharmacokinetic propertiesThalidomide(␣[N=Phthalimido]glutarimide)con-tains a glutarimide moiety with a single chiral center and is formulated as a racemic mixture of two active enantiomers,S(−)and R(+)(see Fig.1).Initially,the S(−)isoform was thought to be the enantiomer pri-marily responsible for the teratogenic effects and the R(−)isoform for the sedative properties.Purification of the R(−)enantiomer was attempted in order to optimize its clinical application,but was eventually not found to be technically feasible secondary to the rapid interconversion of isomers under physiologic con-ditions.Furthermore,both forms were found to be teratogenic in the New Zealand rabbit model,and thus it remains a racemic mixture(Eriksson,Bjorkman,Roth,& Fig.1.Adapted with permission from Macmillan Publishers Ltd:Nature Reviews Cancer,2004(Bartlett et al.,2004);(a)the chemical structure of thalidomide;(b)alteration of the structure of thalidomideby adding an amino(NH2−)group at the4position of the phthaloyl ring to generate the IMiDs CC-5013and CC-4047.For CC-5013,one of the carbonyls(C O)of the4-amino-substituted phthaloyl ring has been removed.M.Melchert,A.List/The International Journal of Biochemistry&Cell Biology39(2007)1489–14991491Hoglund,2000;Fabro,Smith,&Williams,1967).Poor water solubility led to the development of thalidomide exclusively as an oral agent,with peak plasma con-centrations of the drug detected at3–6h(Chen et al., 1989).Upon ingestion,thalidomide undergoes sponta-neous non-enzymatic hydrolytic cleavage into more than 12different metabolites.Thalidomide and its metabo-lites are quickly eliminated in the urine,with a mean elimination half-life of approximately5h.The pharma-cokinetic properties of thalidomide in the presence of renal or hepatic dysfunction are largely unknown.Dos-ing with thalidomide is disease-dependent,with daily oral schedules of50–800mg,demonstrating efficacy in a variety of disease processes.Over the last decade,second-generation IMiD com-pounds have been developed by chemical modification of the structural backbone of thalidomide in order to enhance immunomodulatory potency and minimize the dose-limiting neurotoxic effects.Both lenalidomide and CC-4047are4-amino-gultaramide derivatives of thalidomide in which an amino group was added to the fourth carbon of the phthaloyl ring of the parent com-pound(see Fig.1)(Bartlett,Dredge,&Dalgleish,2004; Teo et al.,2003).Both agents also exist as a racemic mixture of the active S(−)and R(+)forms.Like thalido-mide,they are both administered in daily oral dosing every21–28days of monthly cycles.Renal elimination predominates,and caution is recommended in dosing of patients with impaired creatinine clearance.The ter-minal half-life of lenalidomide and CC-4047after oral administration are reported as3and7h,respectively (Bartlett et al.,2004;Schey et al.,2004).In contrast to thalidomide in which somnolence,constipation,and peripheral neuropathy are common dose-limiting toxic-ities,both lenalidomide and CC-4047lack significant neurosedative toxicity.Dose-limiting neutropenia and thrombocytopenia are the most common toxic sequelae, while venous thromboembolism has been reported with use of all three agents.3.Pharmacodynamic effects3.1.ImmunomodulationThalidomide and its derivatives are potent immunomodulators with biologic effects on both cytokine stimulation and cell-mediated immunity(see Fig.2).One of the key mediators responsible for the anti-inflammatory responses seen with the use of IMiD agents is tumor necrosis factor-alpha(TNF-␣). Thalidomide enhances degradation of TNF-␣mRNA, thus suppressing this pro-inflammatory cytokinerelease Fig.2.Reproduced with permission from Journal of Clinical Oncol-ogy,2004(Kumar et al.,2004).Proposed mechanism of action of thalidomide in cancer illustrated using myeloma as an example. Thalidomide inhibits angiogenesis,enhances effects of the immune system,inhibits binding of tumor cells to stroma,and inhibits various cytokines.Thaliomide may also have direct effects on the tumor.NK: natural killer;TNF:tumor necrosis factor;IL-6:interleukin-6;VEGF: vascular endothelial growth factor;NF-kB:nuclear factor kappa B. from endotoxin-stimulated monocytes and macrophages (Moreira et al.,1993).The effect on TNF-␣is felt to be largely responsible for the clinical benefit seen in patients with inflammatory conditions such as ENL,who have high endogenous TNF-␣production that is suppressed following thalidomide treatment (Sampaio et al.,1993).In addition,both lenalidomide and CC-4047have up to a50,000-fold higher potency than thalidomide as inhibitors of cytokine generation, including suppression of endotoxin-induced TNF-␣secretion(Bartlett et al.,2004;Corral et al.,1999a). Activation of the transcription factor nuclear factor kappa B(NF-kB),a key regulator of TNF-␣and inter-leukin(IL)-8production,is blocked after thalidomide exposure through inhibition of the inhibitor of kappa B (IkB)kinase(Keifer,Guttridge,Ashburner,&Baldwin, 2001).However,the cellular response to IMiD agents is quite complex and lineage and ligand specific,with evidence that TNF-␣generation is actually enhanced in the setting of T-cell activation.This is demonstrable in1492M.Melchert,A.List/The International Journal of Biochemistry&Cell Biology39(2007)1489–1499vitro with upregulation of TNF-␣production by CD4+ and CD8+T-lymphocytes stimulated by anti-CD3 (Marriott et al.,2002).Furthermore,an increase in TNF-␣serum concentration has been reported upon exposure to IMiD agents in early-phase trials involving solid tumors and inflammatory dermatologic diseases such as toxic epidermal necrolysis(Bartlett et al.,2004; Wolkenstein et al.,1998).While the biologic effects of TNF-␣modulation by the IMiD agents may be central to the therapeutic bene-fits seen in a variety of inflammatory conditions,there are several other cytokines that are similarly affected by this class of agents that may play a significant role in immune modulation.Generation of pro-inflammatory enzymes and cytokines,such as cyclooxygenase-2(COX-2), interleukin-1beta(IL-1␤),transforming growth fac-tor(TGF)-␤,and IL-6are suppressed upon exposure to IMiDs,and contribute to the activation of the T-cell receptor(TCR),particularly in the T H1subset (Bartlett et al.,2004;Corral et al.,1999a;Musto,2004). Analogous to TNF-␣modulation,IL-12secretion is sup-pressed by IMiDs when monocytes are stimulated by lipopolysaccharide and is enhanced in the setting of T-cell stimulation(Corral et al.,1999a,1999b).Expansion of both T-cells and NK-cells is promoted by IL-12secre-tion and thus IMiD agents have the potential to be useful adjuncts in the development of cancer vaccines and other immunotherapuetic approaches(Trinchieri,1998).Fur-thermore,IL-12stimulates interferon-␥(IFN-␥)produc-tion and both cytokines have demonstrable anti-tumor activity and anti-angiogenic-activity(Beatty&Paterson, 2001;Qin&Blankenstein,2000;Trinchieri,1998). 3.2.T-cell activationThe immune response to foreign antigens is a highly regulated process requiring the presentation of major histocompatability(MHC)-bound peptides on antigen presenting cells(APCs)to the TCR.Acces-sory molecules,such as B7on APC and CD28on the T-cell surface,provide secondary signals that are vital to the promotion of T-cell responsiveness.These interactions lead to the subsequent activation and pro-liferation of T-cells followed by a cascade of cytokine and cellular responses.Thalidomide and its deriva-tives are able to enhance the CD8+T-cell response in the absence of these secondary co-stimulatory sig-nals(Haslett,Corral,Albert,&Kaplan,1998;Mueller, Jenkins,&Schwartz,1989).In vitro data of primary human T-cells suggest that thalidomide enhances IL-2 mediated T-cell proliferation and IFN-␥production via the TCR complex.The effect of thalidomide on T-cell expansion is dose-dependent and occurs even at low lev-els of CD3stimulation.Furthermore,thalidomide affects the balance between T-helper(Th)-1and-2subsets at least in part through cytokine modulation of IL-4,IL-5,and IFN-␥(McHugh et al.,1995).In the presence of thalidomide,mitogen-and antigen-stimulated human peripheral blood mononuclear cells preferentially induce the Th-2subtype,which corresponds with maximum enhancement of IL-4production.Thalidomide derivatives are also potent co-stimulators of T-cells that enhance activation of CD8+ T-cells in vitro(Stirling,2001).Upon exposure to CMV and influenza virus matrix proteins,both CC-5013and thalidomide were shown to enhance CD8+cytokine production and cytotoxic activity(Haslett,Hanekom, Muller,&Kaplan,2003).CC-4047has demonstrated durable,tumor-specific Th-1type immunity in mice tumor xenograft models(Dredge,Marriott,Todryk et al.,2002).These preclinical investigations have suggested a potential role for the use of IMiD agents in the development of tumor vaccine adjuncts and as modulators of immune response in the setting of defective CD4+mediated immunity such as HIV and graft versus host disease.3.3.AngiogenesisIn the early1990s,thalidomide wasfirst reported to exhibit potent anti-angiogenic properties that were thought to contribute to the teratogenic effects of limb bud malformations observed in offspring of thalidomide exposed gravid mothers(D’Amato,Loughnan,Flynn, &Folkman,1994).Eventually,the effect of IMiDs on vasculogenesis was recognized as a mechanism of poten-tial clinical benefit in the treatment of malignancies in which neoangiogenesis is a conserved feature of the malignant phenotype.Vascular endothelial growth fac-tor(VEGF)and betafibroblast growth factor(bFGF)are potent stromal mitogens that are produced in excess in a variety of malignancies,including multiple myeloma and myeloid disorders.Paracrine and autocrine secre-tion of VEGF causes proliferation of multiple myeloma cell lines and has also been shown to promote self-renewal of leukemia progenitors(Bellamy et al.,2001; Gupta et al.,2001).Secretion of both VEGF and bFGF from tumor and bone marrow stromal cells is sup-pressed upon exposure to IMiDs,resulting in reduced endothelial cell migration and adhesion(D’Amato et al.,1994;Dredge,Marriott,Macdonald et al.,2002; Lentzsch et al.,2003).Both thalidomide and CC-4047 have been shown to suppress the induction of VEGF in co-cultures of multiple myeloma cell lines and boneM.Melchert,A.List/The International Journal of Biochemistry&Cell Biology39(2007)1489–14991493marrow stromal cells(Gupta et al.,2001).Additionally, thalidomide inhibits bFGF-induced angiogenesis in vivo using a rabbit cornea micropocket assay(D’Amato et al.,1994).In murine lymphoma and rectal carcinoma cell line xenografts,IMiDs decrease tumor microvessel formation(Dredge,Marriott,Macdonald et al.,2002; Lentzsch et al.,2003).The latter anti-angiogenic effect is independent of TNF-␣suppression or endothelial cell proliferation,and appears to be dose-or concentration-dependent.Furthermore,lenalidomide has been shown to attenuate AKT-dependent phosphorylation,resulting in a reduction of bFGF-induced endothelial cell migra-tion(Dredge,Marriott,Macdonald et al.,2002;Dredge et al.,2005).3.4.Bone marrow microenvironmentThe pro-inflammatory responses within the bone marrow microenvironment are thought to play a sup-portive or tumor nurturing role in many hematologic diseases,including multiple myeloma and myeloid dis-orders.TNF-␣induces expression of IL-6secretion by bone marrow stromal cells and is markedly upregulated upon adhesion of multiple myeloma cells to bone mar-row stromal cells(Gupta et al.,2001;Witzig,1999). The adhesion molecules,ICAM-1,LFA-1,and VCAM-1,are similarly affected in the bone marrow milieu (Miyamoto et al.,1995).IL-6promotes the prolifera-tion of multiple myeloma cell lines and inhibits Fas-and dexamethasone-induced apoptosis in vitro.Both thalidomide and CC-4047decrease upregulation of IL-6in co-cultures of bone marrow stromal and multiple myeloma cells,suggesting an additional mechanism of therapeutic benefit in multiple myeloma.Lenalido-mide induces activation of cell adhesion molecules and increases␤1integrin-mediated adhesion to extracel-lular matrix proteinfibronectin(Dredge et al.,2005; Miyamoto et al.,1995).3.5.Anti-tumor and apoptotic mechanismsIndependent of the immune-modulating activities, IMiDs have direct anti-proliferative activity in hema-tologic malignancies.The IMiDs,as a class,induce concentration-dependent inhibition of proliferation in multiple myeloma cell lines and primary myeloma cells that are resistant to standard chemotherapy(Lentzsch et al.,2003).Effects on apoptosis are evident at multiple levels of death receptor signaling,including potentia-tion of TNF-related apoptosis-inducing ligand(TRAIL), inhibition of apoptosis protein-2,increased sensitivity to Fas induction,and upregulation of caspase-8activa-tion(Keifer et al.,2001;Mitsiades et al.,2002).G0/G1 cell cycle arrest or apoptosis in leukemia cell lines and other hematologic malignancies occurs with lenalido-mide exposure and is mediated,at least in part,by A-dependent mechanisms(Dredge et al.,2005).Further-more,lenalidomide has preferential anti-proliferative activity against a5q mutant cell line(MUTZ-1)with corresponding induction of expression of genes encoded at the5q locus(Gandhi et al.,2004).These preclinical findings have been confirmed in clinical trials involving patients with myelodysplastic syndromes(MDS).4.Role of IMiDs in cancer therapyThalidomide and its analogs have therapeutic potential in a wide spectrum of diseases given their multifaceted pharmacologic effects.The known immunomodulatory and anti-angiogenic properties of IMiDs provided the impetus to investigate these agents in the treatment of both hematologic malignancies and in solid tumors.Numerous early-phase trials in solid tumors have shown activity in prostate cancer,breast cancer,Kaposi’s sarcoma,renal cell cancer,melanoma, neuroendocrine tumors,hepatocellular carcinoma,lung cancer,and gliomas(Kumar et al.,2004).Response rates have been promising in some;however,further studies are needed to elucidate the true magnitude of thera-peutic benefit in solid tumors.In addition,the IMiDs are attractive agents for the treatment of both myeloid and lymphoid malignancies with reported activity in non-Hodgkin’s lymphoma,acute myeloid leukemia,and myelofibrosis with myeloid metaplasia(Kumar et al., 2004).However,the earliest focus of clinical investiga-tions involved multiple myeloma and MDS and thus will be discussed in further detail.4.1.Multiple myelomaThe use of IMiDs in the treatment of multiple myeloma has recently emerged as the standard of care following multiple reports of efficacy in both front-line therapy and in relapsed or refractory dis-ease(Glasmacher et al.,2006;Rajkumar,Blood,Vesole, Fonseca,&Greipp,2006;Singhal et al.,1999;Tosi, Zamagni,&Cellini,2004).In May2006,thalidomide was approved by the US FDA for the treatment of newly diagnosed multiple myeloma in combination with dex-amethasone.The approval was based on a phase III multicenter trial performed by the Eastern Coopera-tive Oncology Group(ECOG)in which patients were randomized to four cycles of dexamethasone40mg on days1–4,9–12,17–20of28-day cycles either1494M.Melchert,A.List/The International Journal of Biochemistry&Cell Biology39(2007)1489–1499Table1Summary of MM-009and MM-010,phase III trials of CC-5013in multiple myelomaMM-009MM-010North American trial International trialCC-5013+Dex Dex alone CC-5013+Dex Dex alone TTP(weeks)60.120.753.420.6 Overall RR(%)61.222.85821.7CR(%)26.5 4.113.6 4.0 Dex:dexamethasone;TTP:time to progression;RR:response rate;CR:complete response.alone or with200mg daily of thalidomide(Table1) (Rajkumar et al.,2006).Paraprotein responses in serum and urine monoclonal protein levels were observed in63%of patients treated on the combination arm compared to41%of patient receiving dexamethasone alone(p=.0017).Toxicities were significant,with17% of patients developing deep venous thrombosis which prompted the recommendation for anticoagulation dur-ing combination therapy.Other adverse events included rash,bradycardia,and neuropathy.As a consequence,the thalidomide/dexamethasone combination is a common induction regimen for use as initial therapy in multiple myeloma and prior to autologous transplant.Thalidomide has also enjoyed success in the salvage setting,with multiple phase I and II trials demon-strating efficacy either alone with response rates of 25–35%,or in combination with dexamethasone with response rates of50–60%(Glasmacher et al.,2006; Tosi et al.,2004).Combination chemotherapy trials with thalidomide have yielded variable rates of suc-cess in relapsed and refractory disease when applied in conjunction with dexamethasone,cisplatin,adriam-cyin,cyclophosphamide,etoposide,clarithramycin,and melphalan(Coleman et al.,2002;Kyriakou et al.,2005; Lee et al.,2003;Srkalovic,Elson,Trebisky,Karam, &Hussein,2002).Finally,thalidomide has also shown benefit in the maintenance setting.The Intergroupe Fran-cophone du Myelome(IFM)recently reported the results of trial involving597patients who were randomized after autologous stem cell transplantation to three of the treatment strategies,i.e.,either(A)no maintenance, (B)pamidronate maintenance,or(C)thalidomide and pamidronate maintenance treatment until disease pro-gression(Attal et al.,2006).A complete or very good partial response was achieved in55%of patients in arm A,57%in arm B,and67%in arm C(p=0.03).The 3-year post-randomization probability of event-free sur-vival was improved with the thalidomide combination maintenance with36%of patients in arm A,37%in arm B,and52%in arm C remaining without evidence of disease progression(p<.009).The4-year probabil-ity of survival from the date of diagnosis was improved in the thalidomide/pamidronate maintenance arm(77% versus74%versus87%;p<.04).The initial dose of thalidomide was400mg daily,with39%of patients dis-continuing treatment secondary to adverse effects at a median of8months.Thus,while toxicities remain sub-stantial,thalidomide is an effective agent in the treatment of myeloma in all stages of the disease.Of particular importance,maintenance therapy with thalidomide in this trial did not increase the risk of thromboembolic complications,suggesting that thrombogenic potential may be highest when thalidomide is administered dur-ing induction therapy when tumor burden is high or when combined with agents that have intrinsic thrombogenic potential.Lenalidomide was subsequently approved by the FDA in June2006for combination treatment with dex-amethasone for relapsed or refractory multiple myeloma. Based on encouraging data from several phase I and II trials,two phase III randomized,multicenter trials (MM-009,US and MM-010,Europe)were initiated comparing lenalidomide and dexamethasone combi-nation treatment with dexamethasone and placebo in patients with multiple myeloma who had received at least one prior therapy(Weber et al.,2006).Interim results were reported at the American Society of Clinical Oncology Meeting in2006.Lenalidomide was adminis-tered in a daily25mg dose for21days in combination with dexamethasone pulse dose treatment of40mg on days1–4,9–12,and17–20in a28-day cycle.Major reductions in serum paraprotein concentration were reported in51–53%of the lenalidomide/dexamethasone group and were statistically superior to those seen in patients receiving dexamethasone alone(OR 5.5 [3.9,9.1];p<.0001).The median time to progression (TTP)in MM-009compared favorably:37weeks in the lenalidomide/dexamethasone arm versus19.9weeks for dexamethasone alone(HR=0.356[0.257,0.494]; p>.0001).Toxicities were manageable;however,grade 3/4neutropenia and thrombocytopenia were experienced in27%and17%of patients,respectively,with a7.8% incidence of deep vein thrombosis.Importantly,the adverse events commonly seen with thalidomide,such asM.Melchert,A.List/The International Journal of Biochemistry&Cell Biology39(2007)1489–14991495neuropathy,constipation,and sedation,were infrequent in these trials.Other toxicities include included rash, gastrointestinal symptoms,myalgias,and pulmonary embolism.Among patients receiving the lenalidomide combination in the MM-009study,thrombo-embolic events were reported in20of87patients(23%)who received concomitant recombinant erythropoietin ther-apy and in4of83patients who did not receive erythropoietin(5%)(Knight,DeLap,&Zeldis,2006). In the group that received placebo and dexametha-sone,thrombosis occurred in5of67patients(7%) who received concomitant erythropoietin and in1of 103patients(1%)who did not receive erythropoietin. Multivariate analysis of both studies combined showed an independent correlation between the development thrombotic events and treatment with the combination of lenalidomide and high-dose dexamethasone or treatment with concomitant erythropoietin.Of particular interest, thrombotic events were not reported among23patients who received aspirin or salicylates during thefirst month of treatment,as compared with52of668patients who did not receive aspirin or salicylates.A recent study showed a reduction in the thrombosis rate with the administration of aspirin in myeloma patients receiving a combination of thalidomide and anthracycline,sug-gesting that thrombotic risk with the IMiDs may be reduced when used in combination therapy by avoid-ance of recombinant erythropoietins that have inherent thrombotic potential,or prophylaxis with aspirin or alter-nate strategies(Baz et al.,2005).The latter approach is a subject of current investigation in an ECOG study.Dis-tribution of lenalidomide,like its parent compound,is also highly regulated given concerns for possible ter-atogenic effects.All patients prescribed this drug must participate in the Rev-Assist program prior to receiving medication.A phase I,dose-escalation study of CC-4047in multiple myeloma has also been reported with demon-strated safety and efficacy(Schey et al.,2004).The drug was well tolerated,with the main dose-limiting toxic-ities being neutropenia and venous thrombosis with a maximum tolerated dose of2mg/day.A25%or more reduction in paraprotein was seen in67%of patients,and 54%achieved greater than a50%reduction.In support of T-cell activation as possible mechanistic role,increased serum IL-2receptor and IL-12levels were detected in patients receiving CC-4047.4.2.Myelodysplastic syndromesIMiDs were initially targeted as potential agents for the treatment of MDS based on their immunomodula-tory and anti-angiogenic features.Thefirst report of the use of thalidomide in MDS involved a trial of83 patients and included biologic correlates designed to assess angiogenic and inflammatory responses(Raza et al.,2001).Thalidomide was initiated at100mg daily and titrated upwards to a dose of400mg daily as tolerated. At12weeks of treatment,only61%of patients were able to complete the planned course of treatment sec-ondary to dose-limiting toxicities.Only13%of patients experienced a major erythroid response,and platelet or neutrophil improvements were uncommon.How-ever,erythroid responses were durable,with a median duration of306days.Thalidomide has since been inves-tigated in multiple trials at doses of200–1000mg daily in the treatment of both low-and high-risk MDS,with either hematologic improvement or partial responses reported in approximately20–60%of patients(Bouscary et al.,2005;Moreno-Aspitia et al.,2006;Zorat et al.,2001).At these doses,tolerance of thalidomide is discouraging,with a high frequency of dose-limiting fatigue,constipation,neuropathy,and sedation.For this reason,enthusiasm for development of thalidomide in the treatment of MDS has been tempered.In contrast,lenalidomide has shown remarkable activ-ity in the treatment of MDS with toxicities that compare favorably to thalidomide.The initial report on the safety and efficacy of lenalidomide in MDS included 43patients with symptomatic anemia who had either failed treatment with erythropoietin(EPO)or were poor candidates for benefit from EPO therapy(frequent transfusions(>2per month)and/or high endogenous ery-thropoietin serum concentration(>500mU/ml))(List et al.,2005).Patients were randomized to one of three dos-ing schedules:25mg daily,10mg daily,or10mg/day for21of ing the International Work-ing Group(IWG)criteria,56%of patients experienced durable erythroid responses and20of32patients who previously required RBC support became transfusion independent.Furthermore,10of12patients with an isolated interstitial deletion of chromosome5(5q31.1) experienced an erythroid response compared to57%of patients with a normal karyotype or12%of patients with other chromosomal abnormalities.Patients with 5q31.1had particular benefit with a longer duration of transfusion independence.Both cytogenetic responses and decreased medullary myeloblast percentage were noted in patients responding to lenalidomide,and were more pronounced in patients with chromosome5q31.1 deletion.The dose-limiting toxicities were related to myelosuppression,with grade3or greater neutrope-nia(58%)and thrombocytopenia(50%)necessitating dose reductions or treatment interruption in47–77%of。

克劳德·麦凯《回到哈莱姆》中的跨国书写

克劳德·麦凯《回到哈莱姆》中的跨国书写

克劳德•麦凯《回到哈莱姆》中的跨国书写舒进艳内容摘要:克劳德•麦凯的《回到哈莱姆》描摹了20世纪早期的黑人跨国体验。

学界主要阐释了作者个人的跨国经历与黑人国际主义思想对小说塑造主要人物的影响,而忽视了小说中副线主人公雷的国籍及其旅居哈莱姆的意义。

雷的跨国移民经历既再现了麦凯的复杂跨国情感与认同经历,又观照了哈莱姆作为流散非裔移居的理想家园与城市黑人社区所承载的空间意涵。

论文提出哈莱姆具有三个维度,作为移民唤起历史记忆的地理空间、建构跨国身份的政治空间及容纳差异的多元文化空间,并考察移民在跨国流动中历经的现代性体验,以此揭示他们通过改变既定身份与重新定义自我而竭力摆脱传统的民族、种族和阶级观念的束缚与身份认同的困惑,从而参与到美国城市的种族空间生产中。

关键词:克劳德•麦凯;《回到哈莱姆》;跨国书写基金项目:本文系国家社会科学重大项目“美国文学地理的文史考证与学科建构”(项目编号:16ZDA197);天津市研究生科研创新项目“美国新现实主义小说的跨国空间研究”(项目编号:19YJSB039)的阶段性研究成果。

作者简介:舒进艳,南开大学外国语学院博士研究生、喀什大学外国语学院副教授,主要从事美国文学研究。

Title: Claude Mckay’s Transnational Writing in Home to HarlemAbstract: Claude McKay’s Home to Harlem depicts the black transnational experience of the early 20th century. Academics mainly studied the influence of McKay’s personal transnational experience and black internationalist thinking on his main character, but neglected the minor plot’s protagonist Ray and his nationality, and the significance of his sojourn in Harlem. Ray’s transnational migration experience not only embodies McKay’s complex transnational feeling and identity experience, but also reflects Harlem’s spatial significance as an ideal home for African diaspora and urban black community. The paper aims to examine Caribbean immigrants’ experience of modernity in Harlem which is interpreted as the geographic space for immigrants to evoke historical memories, the political space for constructing transnational identities and the multicultural space for accommodating differences. It is to prove that they manage to extricate themselves from the shackles of traditional concepts of nation, race and class and their confusion of identity by changing their established identity and redefining themselves, and thus participate in the production of racial space in American cities.60Foreign Language and Literature Research 2 (2021)外国语文研究2021年第2期Key words: Claude Mckay; Home to Harlem; transnational writingAuthor: Shu Jinyan is Ph. D. candidate at College of Foreign Languages, Nankai University (Tianjin, 300071, China), associate professor at School of Foreign Studies, Kashi University (Kashi 844000, China). Her major academic research interest includes American literature. E-mail: ******************1925年,阿伦•洛克在《新黑人》选集中将哈莱姆描述为一个国际化的文化之都,视其重要性堪比欧洲新兴民族国家的首都。

优质护理在脑梗死患者护理中的应用效果评价

优质护理在脑梗死患者护理中的应用效果评价

review[J].Biomed Pap Med Fac Univ Palacky Olomouc Czech Repub,2012,156:186-199.[12] Lubiński J,Lener MR,Marciniak W,et al.Serum essential elements andsurvival after cancer diagnosis[J].Nutrients,2023,15(11):2611.[13] Schenk JM,Till C,Neuhouser M,et al.Differential biopsy patternsinfluence associations between multivitamin use and prostate cancer risk in the selenium and vitamin e cancer prevention trial[J].Cancer Epidemiol Biomarkers Prev,2022,31:2063-2069.[14] Crowe FL,Appleby PN,Travis RC,et al.Endogenous hormones,nutritionalbiomarkers and prostate cancer collaborative group. Circulating fatty acids and prostate cancer risk: Individual participant meta-analysis of prospective studies[J].J Natl Cancer Inst,2014,106(9):dju240.[15] Parra-SS,Ahumada D,Petermann-Rocha F,et al.Association ofmeat,vegetarian,pescatarian and fish-poultry diets with risk of 19 cancer sites and all cancer:findings from the UK Biobank prospective cohort study and meta-analysis[J].BMC Med,2022,20:79.[16] Birney E.Mendelian randomization[J].Cold Spring Harb PerspectMed,2022,12(4):a041302.[17] Davey SG,Hemani G.Mendelian randomization:genetic anchors for causalinference in epidemiological studies[J].Hum Mol Genet,2014,23:89-98.[18] Dong H,Kong X,Wang X,et al.The causal effect of dietary compositionon the risk of breast cancer: A mendelian randomization study[J].Nutrients,2023,15(11):2586.[19] Yan H,Jin X,Zhang C,et al.Associations between diet and incidencerisk of lung cancer: A Mendelian randomization study[J].Front Nutr,2023,10:1149317.[20] Yin L,Yan H,Chen K,et al.Diet-derived circulating antioxidants andrisk of digestive system tumors: A mendelian randomization study[J].Nutrients,2022,14(16):3274.[21] Brasky TM,Darke AK,Song X,et al.Plasma phospholipid fatty acidsand prostate cancer risk in the SELECT trial[J].J Natl Cancer Inst,2013,105:1132-1141.[22] Outzen M,Tj ønneland A,Christensen J,et al.Fish consumption andprostate cancer risk and mortality in a Danish cohort study[J].Eur J Cancer Prev,2018,27:355-360.[23] Fu YQ,Zheng JS,Yang B,et al.Effect of individual omega-3 fatty acids onthe risk of prostate cancer: A systematic review and dose-response meta-analysis of prospective cohort studies[J].J Epidemiol,2015,25:261-274.[24] Burgess S,Swanson SA,Labrecque JA.are mendelian randomizationinvestigations immune from bias due to reverse causation[J].Eur J Epidemiol,2021,36:253-257.[25] Guo JZ,Xiao Q,Gao S,et al.Review of Mendelian Randomization Studieson Ovarian Cancer[J].Front Oncol,2021,11:681396.[2024-01-07收稿]脑血管疾病是指脑血管病变所引起的脑功能障碍。

普洱茶功效英文版

普洱茶功效英文版

The Efficacy of Puer TeaSince it was discovered, Chinese Tea has been used by the human up to now for its aspects of curative efficacies. Professor Liu Qianliang concludes the curative effect into following aspects: Viz. sleepless , tranquilization, improving eyesight, refreshing, encouraging production of body fluids to extinguishthirst, heat-clearing and detoxifcation , promoting digestion, shun qi, inducing diuresis, relieve constipation, expelling phlegm, dispelling wind-evil, treating cardiodynia, replenishing qi, prolonging the life , etc. The scientific research indicates that the Puer tea has the same function mentioned above as other tea and the modern research proves that it is more prominent in following aspects of curative effect.1. Efficacy of Reducing lipid, weight reduction, antihypertensive and anti-arteriosclerosis.Compared with 31 cases treated by clofibrate, which has good curative effect for hyperlipidemia, 55 cases of clinical tests on curing hyperlipidemia with Yunan puer bowel tea has been made in China Kunming Medical school and the efficacy of Yunnan puer tea is higher than clofibrate. Puer tea can reduce the cholesterol and the glyceride, so drinking Puer tea for a long time has the efficacy of loosing weight. Puer tea could cause the physiological effects such as: vasodilatation,blood pressure decreasing, and heart rate slowing down, brain blood stream reduction.Therefore it has good effects for the patient with hypertension and cerebral arteriosclerosis.2.Efficacy of Anticancer and Preventive Cancer: Professor Hu Meiyinghas conducted the research on the anti-cancer function of puer tea with electron microscope method more than ten years, discovering that Puer tea is most intense to kill the cancer cell; even that 1% of the normal drinking Concentration has the obvious function.Therefore, Puer tea and prevent cancer.3.stomach-nourishing, stomach protection :Under the suitable temperature, drinking the mild Pu'er tea will not stimulate the stomach. Melicera, mellow and plateful Pu’er tea enters the enterogastric and forms the membrane, adhering on the inner surface of gastric to form the useful protective coating.Therefore, long-term Drinking puer tea can nourish and protect the stomach.4.Caring and protecting the teeth; Pu'er tea includes many biologicalactivity ingredient and has the efficacy of sterilization and disinfection. The test has indicated that Puer tea can care and protect the teeth, which will have the best effect at the concentration of 1%.5.Antiphlogosis, sterilization& reliving dysentery: The medicineresearches and the clinical test proves that the Yunnan Pu'er tea hasthe effect of bacteriostasis. Drinking the strong tea ten times per day may treat bacillary dysentery, which has something direct with that Yunnan tea is rich in tea polyphenol .6.Anti-aging:the catechin contained in the tea has the anti-senilefunction. Yunan Puer tea contains more catechin than other teas, so the anti-senile efficacy surpasses other teas. At the same time, the macro-molecule multi-carbohydrate material of Puer tea transforms into massive new soluble monosaccharide and the oligosaccharide and Vitamin C increases in times in the processing of Puer tea. Those materials play a very important role in enhancing the function of immune system of the human body, improving the health and prolong the life.。

彭巴效应作文范文

彭巴效应作文范文

彭巴效应作文范文英文回答:The Penba effect, also known as the "Pemba effect," refers to the phenomenon where hot water freezes faster than cold water. This concept has fascinated scientists and researchers for many years, and there are various theories as to why this occurs.One possible explanation for the Penba effect is the Mpemba effect, which suggests that hot water evaporates more quickly, thus reducing the amount of water that needs to be frozen. This can lead to a faster freezing process overall. Another theory is that hot water contains fewer dissolved gases, which can also contribute to faster freezing.I first learned about the Penba effect in my high school science class. My teacher conducted an experiment where we compared the freezing times of hot and cold water,and sure enough, the hot water froze faster. It was a fascinating experience, and it sparked my curiosity about the science behind this phenomenon.In everyday life, we can see the Penba effect in action when we're making ice cubes. If you're in a hurry and need ice quickly, you might choose to use hot water instead of cold water to speed up the freezing process. This practical application of the Penba effect demonstrates how it can be relevant in our daily lives.中文回答:彭巴效应,也被称为“彭巴效应”,指的是热水比冷水更快地冻结的现象。

栝楼根腐病镰孢菌拮抗菌SJ1623发酵代谢物的抑制活性

栝楼根腐病镰孢菌拮抗菌SJ1623发酵代谢物的抑制活性

栝楼根腐病镰孢菌拮抗菌SJ1623发酵代谢物的抑制活性余利,孟祥涛,陈甦,潘怀松,段海明∗㊀(安徽科技学院,安徽凤阳233100)摘要㊀检测了6株拮抗菌发酵上清液对栝楼根腐病菌的抑制活性,采用菌丝生长速率法测定优势拮抗菌不同接种量和发酵时间对发酵上清液抑菌活性的影响,测定了不同稀释倍数的发酵上清液和脂肽粗提物对栝楼根腐病菌的抑制活性㊂结果表明,对栝楼根腐病菌抑制活性最高的拮抗菌为SJ1623,种子液培养时间为10h ,0.75%(体积比)的接种量效果较好;发酵上清液稀释10倍对病菌的抑制率为87.6%,脂肽粗提物50倍稀释液对病菌的抑制率为83.1%㊂关键词㊀栝楼根腐病;拮抗菌;发酵液;抑制活性中图分类号㊀S 435.67㊀㊀文献标识码㊀A㊀㊀文章编号㊀0517-6611(2024)03-0119-03doi :10.3969/j.issn.0517-6611.2024.03.028㊀㊀㊀㊀㊀开放科学(资源服务)标识码(OSID):Inhibitory Activity of Fermentation Metabolites of Antagonistic Bacteria SJ1623Against Trichosanthes kirilowii Fusarium Root Rot YU Li ,MENG Xiang-tao ,CHEN Su et al㊀(Anhui Science and Technology University,Fengyang,Anhui 233100)Abstract ㊀The inhibitory activity of the fermentation supernatant of 6antagonistic bacteria against Trichosanthes kirilowii Fusarium root rot was detected.The effects of different inoculation amount and fermentation time of the dominant antagonistic bacteria on the antifungal activity of fer-mentation supernatant were determined by the mycelial growth rate method.The inhibitory activity of fermentation supernatant and crude li-popeptide extract against Fusarium sp.was determined.The results showed that the antagonistic bacteria SJ1623had the highest inhibitory ac-tivity.The seed liquid culture time was 10h,and the inoculation amount of 0.75%(volume ratio )was better.The inhibition rate of the fer-mentation supernatant diluted 10times was 87.6%.The inhibition rate of 50times dilution of crude lipopeptide extract was 83.1%.Key words ㊀Trichosanthes kirilowii root rot;Antagonistic bacteria;Fermentation broth;Inhibitory activity基金项目㊀凤阳县科技计划项目(NY2022-05);作物抗逆育种与减灾国家地方联合工程实验室开放基金(NELCOF20190102);安徽省高校自然科学研究项目(KJ2017A510,KJ2019A0814);安徽省重点研究与开发计划项目(202104a06020001)㊂作者简介㊀余利(1985 ),女,贵州习水人,实验师,从事作物栽培和育种研究㊂∗通信作者,副教授,从事作物病害生物防治研究㊂收稿日期㊀2023-02-10㊀㊀栝楼(Trichosanthes kirilowii )是葫芦科栝楼属多年生缠绕性藤本植物㊂栝楼的种子㊁根㊁茎㊁叶㊁瓜皮皆可做优良的中药材,具有解热止渴㊁利尿㊁镇咳祛痰㊁扩张冠状动脉㊁抗肿瘤㊁抑制血小板凝集等药理功能[1-2]㊂栝楼属于多年生宿根植物,一旦地下发生根腐病对其生长造成严重的影响,轻则因营养不良而造成减产,重则引起整株死亡而导致绝收[3]㊂栝楼根腐病的致病因素比较复杂,主要分为生物因素和非生物因素2个方面,其中生物因素主要由病原真菌㊁线虫和细菌引起,而非生物因素则由水分胁迫㊁土壤及其营养元素失衡等造成,二者致病因素混合存在导致根腐病发生更为严重㊂闫龙民等[4]研究表明,栝楼块根中锌和磷的含量越高,根腐病的发病率越低,可通过加施上述2种元素的方法减轻损失㊂栝楼根腐病大多数是由镰孢属真菌(Fusarium sp.)侵染引起,具有明显的积年流行病害的特征,应提早开展防治工作[5]㊂施用多菌灵㊁福美双㊁苯醚甲环唑等化学药剂不能彻底根除该病害的发生,而且连年施用对环境具有较大破坏作用,不利于中药材的药品安全[6]㊂目前,对栝楼等中药材根部病害主要采取生物防治的相关措施,枯草芽孢杆菌(Bacillus subtilis )㊁解淀粉芽孢杆菌(Bacillus amyloliquefa-ciens )㊁哈茨木霉(Trichoderma harzianum )等微生物菌剂以及功能菌发酵制备的生物有机肥已较为广泛地应用于中药材根腐病的防治,在部分地区产生了可观的效果,但应用益生菌防治病害受到菌株种类㊁环境㊁施用方法等的影响较大,总体推广应用面积较小[7]㊂因此,通过系统研究筛选更加高效广适的拮抗菌对于栝楼根腐病的防治具有重要意义㊂笔者以栝楼根腐病菌(Fusarium sp.)为靶标菌,开展拮抗菌株筛选研究,进而为栝楼根腐病的可持续防控提供优良的生防菌株㊂1㊀材料与方法1.1㊀材料1.1.1㊀供试菌株㊂栝楼根腐病菌(Fusarium sp.)㊁细菌菌株SJ1510㊁SJ1519㊁SJ1623㊁GFJ -3㊁D -1和F -1由安徽科技学院植物土传病害生物防治研究室分离纯化并保存㊂1.1.2㊀供试培养基㊂PDA 培养基㊁NA 培养基和NB 培养基参照方中达[8]的方法配制㊂1.2㊀方法1.2.1㊀6株拮抗菌对栝楼根腐病菌的抑制活性及优势菌的生长曲线㊂无菌条件下将6株细菌划线培养至NA 培养基平板上,置于26ħ恒温箱中培养72h,待菌苔长出后接种到装有15mL NB 培养基的试管中,以140r /min 摇培10h,然后用分光光度计以无菌NB 培养基为对照调整OD 600=1.0,然后再以0.2%(体积比)的接种量接种到装有50mL NB 培养基的150mL 三角瓶中,140r /min 摇培72h,得到菌株的发酵液置于4ħ㊁10000r /min 的离心机中离心10min 得到上清液㊂吸取5mL 发酵上清液和2.5mL 1000mg /L 硫酸链霉素水溶液同时加入42.5mL 冷却到40~60ħ的PDA 培养基中,迅速充分混匀后倒3个平板,对照加入等量和上述浓度相同的硫酸链霉素溶液和5mL 灭菌水,重复3次㊂待平板凝固,接种培养144h 菌落边缘的菌饼(直径为7mm),然后置于26ħ恒温培养箱中连续培养144h 后测量菌落直径,求出不同菌株发酵上清液对病菌的抑制率,优选出抑制效果较好的拮抗菌株用于以下试验㊂1.2.2㊀不同接种量对病菌的抑制活性影响测定㊂按照安徽农业科学,J.Anhui Agric.Sci.2024,52(3):119-121㊀㊀㊀1.2.1 制备的种子液按照0.0625%㊁0.1250%㊁0.2500%㊁0.7500%㊁1.0000%㊁1.5000%(体积比)的接种量接种到装有50mL NB培养基的150mL三角瓶中摇培,同样按照 1.2.1 的方法制备发酵上清液,检测不同接种量制备的发酵上清液对病菌抑制活性的影响㊂1.2.3㊀不同发酵时间对病菌的抑制活性影响测定㊂按 1.2.1 和 1.2.2 优化试验条件开展不同培养时间对病菌抑制活性的影响㊂接种完毕后,发酵摇培时间分别为24㊁48㊁60㊁72㊁84㊁96和120h,检测不同发酵培养时间制备的发酵上清液对病菌抑制活性的影响㊂1.2.4㊀不同稀释倍数的发酵上清液对栝楼根腐病菌的抑制活性测定㊂参照 1.2.1 的方法检测最优条件下制备的发酵上清液原液和原液的1.5㊁3.0㊁4.0和8.0倍稀释液的抑菌活性,然后求出不同浓度的发酵上清液对病菌的抑制率㊂1.2.5㊀不同脂肽粗提物对栝楼根腐病菌的抑制活性测定㊂采用邓建良等[9]方法略有改进制备脂肽粗提物㊂将脂肽粗提物分别稀释5㊁7㊁10㊁15㊁20和40倍,脂肽粗提物的抑菌活性检测方法同 1.2.4 发酵上清液的检测方法㊂1.3㊀抑制率计算公式以及数据分析㊀抑菌率=(对照菌饼直径-处理菌饼直径)/(对照菌饼直径-菌饼直径)ˑ100%;所得数据采用Excel2007和IBM SPSS statistics25.0进行分析㊂2㊀结果与分析2.1㊀6株拮抗菌发酵上清液对栝楼根腐病菌的抑制效果㊀从表1可以看出,6株拮抗细菌对栝楼根腐病菌的抑制率从高到低的顺序为SJ1623㊁SJ1519㊁D-1㊁GFJ-3㊁F-1和GFJ1510㊂其中SJ1623的抑制效果最好,抑制率达82.1%, GFJ1510的抑制效果最差为44.6%㊂筛选出菌株SJ1623作为下一步的研究对象㊂表1㊀6株细菌发酵上清液对栝楼根腐病菌的抑菌效果Table1㊀Antifungal effect of fermentation supernatant of6strains on Fusarium sp.菌株Strain 发酵上清液浓度Concenration of fermentation supernatantʊmL/L抑菌率Inhibition rateʊ%GFJ151010044.6ʃ1.2F-110051.0ʃ1.5 GFJ-310055.8ʃ2.5D-110057.6ʃ1.1SJ151910071.5ʃ0.7SJ162310082.1ʃ1.82.2㊀拮抗菌SJ1623的生长曲线㊀由图1可知,0~6h为菌株生长的延滞期,6~14h为对数生长期,然后进入稳定期㊂因此,选定菌株对数生长的中期10h作为种子液的培养时间㊂2.3㊀拮抗菌SJ1623不同接种量的发酵上清液对病菌的抑制活性㊀由图2可知,随着接种量的不断增加,拮抗菌产发酵上清液的抑制率呈逐渐上升后下降的趋势㊂接种量为0.7500%(体积比)抑制率达最高为85.74%,接种量为图1㊀拮抗菌SJ1623的生长曲线Fig.1㊀Growth curve of antagonistic bacteria SJ1623 0.0625%抑制率最小为62.85%㊂由此可知,初始接种量对发酵上清液抑制活性的影响较大,当接种量较小时菌体增殖较慢,产生的抑菌物质较少;然而接种量过大对抑菌物质的产生同样不利,推测接种量过大导致发酵培养基中的基质营养物消耗过快,导致营养物缺乏或溶氧不足,从而使抑菌效果下降㊂图2㊀不同接种量对发酵上清液抑菌活性的影响Fig.2㊀Effect of different inoculation amount on the antifungal activity of fermentation supernatant2.4㊀拮抗菌SJ1623不同发酵培养时间的发酵上清液对病菌的抑制活性㊀由图3可知,随着培养时间的延长,拮抗菌产发酵上清液的抑制率逐渐上升后缓慢下降㊂培养时长为84h时抑制率最高为87.13%,培养时长为24h抑制率最小为39.58%㊂说明培养时间过短,菌量少抑菌活性物质产生少,但随着培养时间增加,菌量进一步增大,可能由于大量菌体的存在致使抑菌活性物质被菌体吸附而抑菌效果下降,也图3㊀不同培养时间对发酵上清液抑菌活性的影响Fig.3㊀Effect of different culture times on the antifungal activity of fermentation supernatant021㊀㊀㊀㊀㊀㊀㊀㊀㊀㊀安徽农业科学㊀㊀㊀㊀㊀㊀㊀㊀㊀㊀㊀㊀㊀㊀㊀㊀㊀㊀㊀㊀㊀㊀㊀㊀㊀2024年有可能是抑菌物质被进一步分解转化为其他抑菌活性下降的物质㊂2.5㊀拮抗菌SJ1623发酵上清液对栝楼根腐病菌的抑制活性㊀由表2可知,SJ1623发酵上清液的浓度从12.5mL/L增至100.0mL/L时,发酵上清液对栝楼根腐病菌的抑菌率从40.2%增至87.6%,说明发酵上清液对栝楼根腐病菌具有较高的活性,稀释倍数小于15倍所达到的抑菌效果较好㊂表2㊀拮抗菌SJ1623发酵上清液对病菌的抑制活性Table2㊀Inhibitory activity of fermentation supernatant of strain SJ1623against Fusarium sp.稀释倍数Dilution ratio 发酵上清液浓度Concenration of fermentation supernatantʊmL/L抑菌率Inhibition rateʊ%8012.540.2ʃ1.1 4025.048.1ʃ0.5 3033.356.8ʃ1.3 1566.773.5ʃ1.4 10100.087.6ʃ0.22.6㊀拮抗菌SJ1623脂肽粗提物对栝楼根腐病菌的抑制活性㊀由表3可知,从发酵上清液中提取的脂肽粗提物对栝楼根腐病菌的抑制效果明显高于发酵上清液对病菌的抑制效果,50倍稀释液的抑菌率可达83.1%㊂然后随着稀释倍数的增加抑菌率开始降低,因而对病菌要有较高的抑制效果,其稀释倍数应小于70倍㊂表3㊀拮抗菌SJ1623产脂肽粗提物对病菌的抑制活性Table3㊀Inhibitory activity of crude lipopeptide extract from antago-nistic strain SJ1623against Fusarium sp.稀释倍数Dilution ratio 脂肽粗提物浓度Concentrationof crude lipopep-tide extractʊmL/L抑菌率Inhibitionrateʊ%5020.083.1ʃ0.5 7014.375.3ʃ1.2 10010.064.3ʃ0.8 150 6.754.6ʃ2.6 200 5.049.0ʃ2.2 400 2.528.5ʃ2.83㊀结论与讨论近年来,栝楼种植效益较高,种植面积扩大较快,但由于栝楼为多年生宿根植物,为根部病害的发生创造了良好条件[10]㊂栝楼根腐病的发生受到多重因素的影响,应全方位考虑㊂如不合理灌溉施肥导致土壤酸化,土壤微生物群落结构失调导致土壤微生物多样性降低㊁种群结构简单,有益微生物的生长受到抑制,有益菌逐渐受到有害菌的排斥,从而使土壤从细菌主导型向真菌主导型转化,最终导致以根腐病为代表的土传病害愈演愈烈[11]㊂生物防治措施作为延缓土传病害发生的治本措施,已形成诸多重要成果,也为营造绿色可持续的农业生产环境提供了重要实践路径[12]㊂栝楼根腐病的生物防治措施报道较少,但其主要致病菌 镰孢菌(Fusarium sp.)为代表的葫芦科植物根腐病相关生物防治研究较多㊂曹云娥等[13]采用平板对峙法结合抑制菌丝生长速率法,从蚯蚓堆肥中筛选到1株对4种瓜类枯萎病菌均有显著抑制效果的拮抗细菌WQ-6,经鉴定为暹罗芽孢杆菌(Bacillus siamensis),其对瓜类枯萎病菌具有广谱性防效,发酵液10倍稀释液的抑菌率为34.96%~46.75%;张涵等[14]从河南南阳桐柏山景区土壤中分离筛选到一株对苦瓜枯萎病菌具有抑制效果的短短芽孢杆菌(Brevibacillus brevis TB17),发酵液10倍无菌滤液对病菌的抑制率为54.95%,盆栽防效达76.92%㊂该研究所得的菌株SJ1623的发酵上清液10倍稀释液的室内菌丝生长抑制率达80%以上,说明其应用价值更大,活体试验需要进一步探究㊂脂肽类物质为拮抗细菌发酵液中提取的重要抑菌活性物质[15]㊂向亚萍等[16]报道芽孢杆菌产脂肽类抗生素是抑制植物病原真菌的主要成分,其中伊枯草菌素(iturins)的结构变化及其分泌量与抑菌活性具有相关性㊂该研究所提取的脂肽类物质对栝楼根腐病菌的抑制活性明显高于发酵上清液,同样也说明脂肽类物质在抑菌方面发挥重要作用,下一步应研究脂肽类物质中起主要抑菌作用的活性成分,从而为菌株的开发利用提供基础数据㊂参考文献[1]王力玄,杨磊磊,郭颖婕,等.栝楼化学成分及药理作用研究进展[J].特产研究,2020,42(2):79-84.[2]王楠,汤俊瑜,李怡洁,等.云南栝楼属植物的化学成分及生物活性研究进展[J].安徽农业科学,2022,50(22):1-5.[3]巢志茂.瓜蒌栽培生产和加工贮存环节病虫害防治研究进展[J].中国中医药信息杂志,2009,16(9):100-102.[4]闫龙民,车勇.某些矿物质元素与栝楼根腐病的关系[J].特产研究, 2000,22(2):37-38,43.[5]薛玲,吴洵耻,姜广正,等.栝楼根腐病病原菌的研究[J].山东农业大学学报,1992,23(4):415-420.[6]廖长宏,陈军文,吕婉婉,等.根和根茎类药用植物根腐病研究进展[J].中药材,2017,40(2):492-497.[7]魏蕾.根际微生物防治土传病害研究进展[J].蔬菜,2022(11):32-39.[8]方中达.植病研究方法[M].北京:中国农业出版社,1995:152.[9]邓建良,刘红彦,刘玉霞,等.解淀粉芽孢杆菌YN-1抑制植物病原真菌活性物质鉴定[J].植物病理学报,2010,40(2):202-209.[10]邢站,赵红艳,刘坤,等.瓜蒌规范化生产操作规程[J].山东农机化, 2014(4):39-41.[11]程国亭,王延峰,姜文婷,等.设施番茄土壤障碍综合防控研究进展[J].中国蔬菜,2023(2):16-24.[12]LUONGO L,GALLI M,CORAZZA L,et al.Potential of fungal antagonists for biocontrol of Fusarium spp.in wheat and maize through competition in crop debris[J].Biocontrol science and technology,2005,15(3):229-242.[13]曹云娥,吴庆,张美君,等.瓜类枯萎病生防菌WQ-6的筛选鉴定㊁发酵工艺优化及防效研究[J].园艺学报,2020,47(6):1072-1086. [14]张涵,赵莹,仲荣荣,等.生防细菌TB17的筛选㊁鉴定及其对苦瓜枯萎病的生防作用[J].河南农业大学学报,2022,56(3):429-437. [15]王伟宸,赵进,黄薇颐,等.芽胞杆菌代谢产物防治三种常见植物病原真菌的研究进展[J].生物技术通报,2023,39(3):59-68.[16]向亚萍,陈志谊,罗楚平,等.芽孢杆菌的抑菌活性与其产脂肽类抗生素的相关性[J].中国农业科学,2015,48(20):4064-4076.12152卷3期㊀㊀㊀㊀㊀㊀㊀㊀㊀㊀㊀㊀㊀余利等㊀栝楼根腐病镰孢菌拮抗菌SJ1623发酵代谢物的抑制活性。

荒漠河岸多枝柽柳灌丛碳氮磷化学计量特征及其影响因素

荒漠河岸多枝柽柳灌丛碳氮磷化学计量特征及其影响因素

Vol.34,No.3Mar.,2021第34卷第3期2021年3月环境科学研究Research of Environmental Sciences荒漠河岸多枝桂柳灌丛碳氮磷化学计量特征及其影响因素张晓龙,周继华2,来利明2,姜联合2,郑元润2”1. 山西财经大学资源环境学院,山西太原0300062. 中国科学院植物研究所,北京100093摘要:为了解群落水平下荒漠河岸多枝柽柳(Tamarw ramosissima Ledeb.)灌丛的碳氮磷化学计量特征及其影响因素,在黑河下游荒漠河岸3 800 m 范围内,沿垂直河道方向上设置9个采样点,采用相关性分析、冗余分析(RDA)和偏冗余分析(pRDA)方法,对多枝柽柳群落的碳氮磷化学计量格局及其与环境因子的关系进行研究.结果表明:黑河下游荒漠河岸多枝柽柳群落TC 、TN 、TP 含量平均值分别为380. 27,30. 42和1. 54 mg/g,C :N 、C :P 和N :P 平均值分别为12. 98,257. 09和20. 04.与全球和区域尺度物种水平研究相比,黑河下游荒漠河岸多枝柽柳灌丛群落具有较低的TC 含量、较高的TN 含量和N :P 以及相对稳定的TP 含量.多枝柽柳灌丛群落碳氮磷化学计量特征变异系数相对较小,内稳性较强,相对较高的N :P(14. 55〜27. 20)表明群落水平下多枝 柽柳灌丛更倾向于受磷元素的限制.在沿河梯度上,多枝柽柳群落TC 含量和TN 含量均随沿河距离的增加呈显著下降的变化趋 势,而C :N 随沿河距离的增加呈波动上升的变化趋势;TP 含量呈先降后升的变化趋势,而C :P 和N :P 大致呈先上升后下降的变化趋势.多枝柽柳灌丛群落的碳氮磷化学计量特征与土壤理化属性存在一定相关性,土壤含水量、土壤容重和土壤pH 是影响多 枝柽柳群落碳氮磷化学计量特征变化的关键因子,三者共同解释了总变异的57. 7%,其中土壤含水量解释了总变异的32.8%.研究显示,土壤水盐与多枝柽柳灌丛的碳氮磷化学计量特征关系密切,土壤含水量在解释多枝柽柳灌丛碳氮磷化学计量特征变化方面比土壤pH 更为重要.关键词:荒漠河岸;黑河;多枝柽柳群落;碳氮磷;化学计量特征中图分类号:X171. 1文章编号:1001-6929(2021)03-0698-09文献标志码:A DOI : 10. 13198/j. issn. 1001-6929. 2020. 08. 04Carbon , Nitrogen and Phosphorus Stoichiometric Characteristics of Tamarix ramosissima Ledeb. Shrubland and Their Influencing Factors in a Desert Riparian Area of ChinaZHANG Xiaolong 1,2, ZHOL Jihua 2, LAI Liming 2, JIANG Lianhe 2, ZHENG Yuanrun 2*收稿日期:2020-03-31 修订日期:2020-08-20作者简介:张晓龙( 1988-),男,山西浑源人,讲师,博士,主要从事化学计量生态和生物化学地理研究,***********************.cn .*责任作者,郑元润( 1968-),男,山西大同人,研究员,博士,博导,主要从事植被生态学研究,****************.cn基金项目:国家自然科学基金项目(No.91425301)Supported by National Natural Science Foundation of China (No.91425301)1. School of Resources and Environment , Shanxi Lniversity of Finance and Economics , Taiyuan 030006, China2.Institute of Botany, Chinese Academy of Sciences, Beijing 100093, ChinaAbstract : In order to explore the community level stoichiometric characteristics of Tamarin ramosissima Ledeb. shrubland and their influencing factors in an arid desert riparian area, 9 sites were vertically sampled within 3800 m from the downstream of Heihe River. Thestoichiometric patterns of carbon , nitrogen and phosphorus in a T. ramosissi m a community and their relationship with environmental factorswere studied by correlation analysis , redundancy analysis ( RDA ) and partial redundancy analysis (pRDA). The results show the mean TC , TN and TP contents for the T. ramosissi m a community were 380. 27, 30. 42 and 1. 54 mg/g, respectively. The mean C :N, C :P and N :P ratios for the T. ramosissi m a community were 12. 98, 257. 09 and 20. 04, respectively. Compared to the results of species level at the global and regional scales , the T. ramosi s sima community was characterized by lower TC , higher TN and N :P, and relatively stable TP contents. The variation coefficients of the community level stoichiometric characteristics were much lower and their stoichiometrichomeostasis was relatively strong. The relatively high N : P levels ( 14.55-27.20) indicate that the T. ramosissi m a community might be more heavily limited by P at the community level. Along the river gradient, the TC and TN contents in the T. ramos ss ma communitydecreased significantly with distance from the river, but the C : N ratio increased and fluctuated with distance. The TP content of the community decreased and then increased, while the C : P and N : P ratios increased and then decreased with distance. The stoichiometric第3期张晓龙等:荒漠河岸多枝柽柳灌丛碳氮磷化学计量特征及其影响因素699characteristics and soil physicochemical properties were correlated,and RDA analysis demonstrates that the soil water content,soil bulk density and soil pH had significant impacts on the stoichiometric characteristics of the71.ramosissima community and jointly accounted for 57.7%of the total variation,of which soil moisture accounted for32.8%.Our observations indicate that soil water and saline-alkali properties were closely related to the stoichiometric characteristics of the71.ramosissima shrubland and that soil water content had a stronger impact on the community stoichiometry variations than soil pH.Keywords:desert riparian;Heihe River;Tamarix ramosissima community;carbon,nitrogen and phosphorus;stoichiometric characteristics生态化学计量学作为一门探索生态过程中能量和多重化学元素平衡的新兴学科,为探究植物生长和养分供应关系以及植物与环境之间化学元素的相互耦合性提供了一种综合方法[1-2].碳、氮、磷是植物生长发育和生理生态活动所需的重要元素,植物吸收氮元素、磷元素,同化碳元素,进而影响群落、生态系统的碳过程以及矿质元素的生物地球化学循环[3-4]•相比于其他元素而言,碳、氮和磷元素的耦合作用更强, C:N:P计量比不仅能够反映植物的养分限制状况和适应策略,同时能反映出植物吸收氮和磷过程中的光合固碳能力[5-6].有研究表明,低C:N和C:P的植物倾向于采取高光合速率的竞争策略,而高C:N和C:P的植物更倾向于采用低光合速率的强大防御生态策略[7-8].因此,基于生态化学计量特征的植物-环境关系研究,能更好地揭示不同环境植物群落养分获取及其对环境的适应机制[9].值得提出的是,尽管目前对森林、草原、荒漠和水生生态系统的植物化学计量特征进行了一些有意义的探讨[3,10-11],但对灌丛群落化学计量特征及其对环境梯度变化响应规律的研究仍较少,尤其缺乏对干旱区固沙灌丛的生态化学计量研究[12-13].多枝柽柳(Tamarix ramosissima Ledeb.)具有很强的耐旱性和适应能力,在长期的植被-环境相互作用下发展成不同的群落类型,在维持当地生态系统稳定和提供关键生态系统服务方面发挥着独特的作用[14].有研究表明,在相对潮湿的河岸地带,多枝柽柳具有强烈的水分竞争和向土壤中分泌盐的能力,尤其会限制草本植物的生长,形成单优势种植物群落,从而降低当地生物多样性[15].然而,在相对干旱的荒漠地区,多枝柽柳通过根系的“提水作用”将水分从深层土壤和地下水输送到浅层土壤,水分和养分富集形成“沃岛效应”,通过“沃岛效应”为干旱荒漠地区动植物提供良好的栖息地,从而提高生物多样性[16].以往关于柽柳的研究多集中于植物群落生态学特性及其与环境因子关系方面,例如,地下水变化对柽柳群落多样性的影响[",17]、土壤水分变化对柽柳群落特征的影响[18-19],人工生态输水工程对荒漠河岸柽柳植被恢复的影响[20-21]以及柽柳沙包与环境因子之间的关系[22]等,而对柽柳群落的生态化学计量学研究比较缺乏[8,23].在当前环境条件下,尤其是在极端干旱的荒漠河岸地区,群落水平上柽柳群落碳氮磷化学计量及其相互作用有哪些特点土壤水盐和养分等环境因子如何对柽柳群落碳氮磷化学计量特征产生影响定量地揭示它们之间的相互作用关系将有助于深入认识荒漠河岸地区柽柳群落的养分限制状况和适应策略.鉴于此,该文通过对黑河下游荒漠河岸地带多枝柽柳群落进行调查,分析群落水平下碳氮磷化学计量特征,探讨多枝柽柳群落碳氮磷化学计量格局与环境因子的关系,从而阐明多枝柽柳群落对极端干旱环境的适应性,以期为荒漠河岸柽柳植被恢复和柽柳群落多样性保护提供参考.1材料与方法1.1研究区概况研究区域位于黑河下游荒漠河岸地带(42°06'N〜42°07'N、101°00'E~101°03'E),地处中纬度温带大陆性干旱气候区,气候极端干旱[8].年均温8弋左右,多年平均降水量低于40mm,75%以上的年降水量集中在7—8月,年蒸发量为2300~3700mm[14].下游荒漠河岸地带性土壤为灰棕漠土,两岸发育有林灌草甸土,由于成土过程受地下水影响较大,呈现一定的盐碱化[24].受河流补给地下水的影响,荒漠河岸林主要分布在河岸两边,以胡杨(PopuZus eupAratica)和柽柳(Tamarix ramosissima以旱生和沙生类型的灌木为主,代表性植物有泡泡刺(Nitraria spAaerocarpa)、琵琶柴(Keaumuria soongarica)、细枝盐爪爪(KaZidium graci'Ze)、膜果麻黄(£pAedra przewaZsiii)等[25]•1.2采样点设置与取样2019年8月9—18日植物生长旺季,多枝柽柳处于夏花期(6—9月),在黑河下游乌兰图格沿河监测断面,沿垂直于河岸大致以500m为间隔设置调查样地,共布设群落调查样地9个(见图1).每个样地随机设置3个10mX10m的灌木样方,调查样方内700环境科学研究第34卷所有物种,在灌木、草本层主要记录种类名称、株(丛)数、高度、冠幅、基径和盖度等群落特征;同时记录样地基本状况,包括样地经纬度、坡度、生境、地貌和土地利用等属性.对于每个样方,每个物种地上生物量的测定采用样株收获法,每个物种取2~3株具有代表性的植株带回实验室,用毛刷刷净植株表面的尘土等杂质,于80t恒温烘干至恒质量并称量,进而估算调查样方地上生物量.获取生物量后,将植株粉碎后过0.149mm筛,用于化学性质分析,植物化学性质采用质量百分比表示,植物TC、TN、TP含量测定参照ZHANG等[8]所述方法测定.在与植物群落相对应的样地内,对其土壤理化性质(土壤含水量、容重、TC含量、TN含量、C:N、速效磷含量、pH和电导率)进行测定,取样深度为50cm,每个样地设3个重复,土壤理化属性测定参照ZHANG等[8]所述方法测定.图1研究区样地位置示意Fig.1Locations of the sample plots1.3数据统计分析植物群落TC、TN和TP含量是群落内物种TC、TN和TP含量的加权平均值[11-12].群落TC含量(T c):sT c二工(5G)(1)/二1群落TN含量(T n):sT N二工(5M)(2)/二1群落TP含量(T p):ST p二工(B i P i)(3)/二1式中:S为物种数;B i为物种i的相对地上生物量;C i 为物种i的TC含量,mg/g;N,为种物i的TN含量,mg/g;P i为物种i的TP含量,mg/g.采用SPSS18.0软件进行数据统计分析,用单因素分析和LSD检验法对沿河不同样地多枝柽柳群落的盖度、生物量、TC、TN、TP含量及C:N:P计量比进行差异显著性检验(P<0.05),通过Pearson相关系数分析多枝柽柳群落TC、TN、TP含量及C:N:P计量比与土壤理化属性的关系(P<0.05).为定量分析土壤因子对多枝柽柳群落碳氮磷化学计量特征的影响,采用排序法确定主要影响因子,DCA结果显示,所有排序轴梯度长度均小于3,因此采用冗余分析法(RDA)确定主要影响因子.为避免冗余变量的影响,采用Monte Carlo检验(9999次置换)检测多枝柽柳群落碳氮磷化学计量特征和土壤因子是否存在显著相关关系,排除影响不显著的变量(P>0.05).采用偏冗余分析(“RDA)用于揭示土壤因子对多枝柽柳群落碳氮磷化学计量特征的单独影响与交互作用.上述统计分析在CANOCO5.0软件中完成[26].2结果与分析2.1荒漠河岸多枝柽柳群落基本特征在沿河梯度上,多枝柽柳群落盖度(F=83.18, P<0.001)、地上生物量(F=63.52,P<0.001)在不同样地间均具有显著差异,群落盖度为16.19%~ 85.33%,地上生物量为161.49-2812.81g/m2(见表1).群落盖度和地上生物量随沿河距离的增加呈下降的变化趋势,地上生物量最大值出现在距河100m 处,而群落盖度最大值出现距河1300m处(见表1).2.2荒漠河岸多枝柽柳群落碳氮磷化学计量特征在沿河梯度上,多枝柽柳群落TC含量(F= 10.05,P<0.001)、TN含量(F=12.24,P<0.001)、TP 含量(F=44.73,P<0.001),C:N(F=12.90,P< 0.001)、C:P(F=9.65,P<0.001)和N:P(F=5.11, P=0.002)在不同样地间均具有显著差异(见表2).多枝柽柳群落TC含量为317.39〜439.73mg/g,TN 含量为21.27-43.61mg/g,TP含量为0.97〜2.15 mg/g,C:N、C:P和N:P分别为9.08〜16.52,182.07~ 410.06和14.55〜27.20(见表2).在沿河梯度上,多枝柽柳群落TC和TN含量均随沿河距离的增加呈显著下降的变化趋势,最大值出现在距河100m处,分别为423.67和40.89mg/g;群落TP含量呈先下降后上升的变化趋势(见图2),最大值出现在距河300m处,为2.09mg/g.C:N随沿河距离的增加呈波动上升的变化趋势,最大值出现在距河3800m处,为16.18;而C:P和N:P均大致呈先上升后下降的变化趋势,分别出现在距河1800和2300m处,分别为336.36和24.10(见图2).2.3多枝柽柳群落计量学特征与土壤因子的关系在沿河梯度上,多枝柽柳群落TC含量、TN含量与土壤含水量、土壤TC含量、土壤TN含量和土壤速效磷含量均呈显著正相关,群落TP含量与土壤含水量、土壤TC含量、土壤TN含量和土壤pH均呈显著第3期张晓龙等:荒漠河岸多枝柽柳灌丛碳氮磷化学计量特征及其影响因素701表1黑河下游沿河多枝桂柳样地基本情况注:不同字母表示差异显著(P <0. 05).下同.Table 1 Characteristics of T. ramosissima sites along the downstream of the Heihe River样地编号沿河距离/m海拔/m群落结构盖度地上生物量/( g/m 2 )T1100926灌木-草本结构56. 73%±5. 66%b 2 812. 81±199. 00a T2300926灌木-草本结构67. 57%±3. 38%b2 627. 35±185. 88aT3800925灌木-草本结构75. 04%±1.99%ab 1 969. 46±189. 93b T41 300924灌木-草本结构85. 33%±1.92%a745. 60±39. 06cT51 800924灌木-草本结构45. 14%±2. 80%c 277. 84±8. 39dT62 300923灌木-草本结构32. 59%±4. 79%d389. 63±96. 17d T72 800925单-灌木结构20. 78%±1.05%de 454. 36±38. 92cdT83 300923单-灌木结构21. 65%±3. 15%de316. 15±44. 23d T93 800923灌木-草本结构16. 19%±0. 49%e161.49±20. 28d表2荒漠河岸多枝桂柳样地间群落化学计量特征的方差分析Table 2 The variance analysis community stoichiometric traits at different T. ramosissima sites参数平均值标准差变异系数最小值最大值自由度F P 群落TC 含量/(mg/g)380. 2731.170. 08317. 39439. 73810. 050. 001群落TN 含量/(mg/g)30. 427. 210. 2421.2743. 61812. 240. 001群落 TP 含量/( mg/g)1.540. 360. 230. 97 2. 15844. 730. 001群落C :N 12. 98 2. 290. 189. 0816. 52812. 900. 001群落C :P 257. 0954. 610. 21182. 07410. 0689. 650. 001群落N :P20. 043. 780. 1914. 5527. 2085. 110. 002沿河距离/m 沿河距离/m 沿河距离/m图2多枝桂柳群落全碳、全氮、全磷及碳氮磷计量比随沿河梯度的变化Fig.2 Changes in the T. ramosissima community TC , TN , TP and C :N :P stoichiometricratios along the rivergradient702环 境 科 学 研 究第 34 卷正相关,而群落TP 含量与土壤电导率呈显著负相关(见表3).群落C :N 与土壤容重、土壤C :N 均呈显著正相关,而与土壤含水量、土壤TC 含量、土壤TN 含量和土壤速效磷含量均呈显著负相关;群落C :P 与 土壤电导率呈显著正相关,而与土壤含水量、土壤TC含量、土壤TN 含量和土壤pH 均呈显著负相关;群落N :P 与土壤容重、土壤C :N 均呈显著负相关(见表3).2.4 土壤因子对多枝柽柳群落计量学特征的影响表3多枝桂柳群落碳氮磷化学计量特征与土壤因子之间的相关关系Table 3 Pearson correlation between the T. ramos i ssi m a community stoichiometric traits and soil properties注:* 表示 P <0. 05 ; ** 表示 P <0. 01.项目土壤含水量土壤容重土壤 TC 含量土壤 TN 含量土壤 C :N土壤速效磷含量土壤 pH土壤电导率群落 TC 含量0. 738 **-0. 3540. 813**0. 543 **-0. 0200. 623 **0. 275-0. 262群落 TN 含量0. 828 **-0. 3700. 838 **0. 757 **-0. 3800. 541 **0. 291-0. 287群落 TP 含量0.814**0. 0530. 699 **0. 621 **-0. 0610. 3530. 540 **-0. 550**群落 C :N—0.699 **0. 289 *-0. 681 **-0. 726 **0. 542 **-0. 440 **-0. 1890. 185群落C :P -0.582**-0. 246-0. 382*-0.416*0. 016-0. 134-0.514**0. 523 **群落N :P -0.018-0. 555 *0. 1670. 170-0. 422*0. 239-0. 3420. 342从RDA 排序结果来看,前2个排序轴分别解释 了多枝柽柳群落计量学特征变化的50. 83%和 26. 00%(见图3).排序轴1主要解释了土壤含水量 (F 二20. 3,P <0. 001)和土壤 pH (F 二3. 7,P <0. 05)对柽柳群落计量学特征变化的影响,排序轴2主要解释了土壤容重(F 二9. 0,P <0. 001)对多枝柽柳群落计量学特征变化的影响(见图3).该结果表明,对多枝柽 柳群落计量学特征变化具有显著影响的土壤因子为SBD1.0N :P-l.ol --------------------------------------------------------------------------1.0-0.50.5 1.0轴 1(50.83%)注:TC —群落TC 含量;TN —群落TN 含量;TP —群落TP 含量;C :N —群落 C :N ;C :P —群落 C :P ;N :P —群落 N :P ;SCN —土壤 C :N ; SBD —土壤容重;pH —土壤 pH ; SM —土壤含水量;STN —土壤TN 含量;STC —土壤TC 含量;SAP —土壤速效磷含量;SEC —土壤电导率.图3多枝桂柳群落碳氮磷化学计量特征与土壤因子RDA 排序结果Fig.3 RDA ordination plot of the T. ramos ss macommunity stoichiometric traits and soil properties土壤含水量、土壤容重和土壤pH.偏冗余分析表明, 土壤含水量、土壤容重和土壤pH 共同解释了多枝柽柳群落计量学特征变化的57. 7%, 土壤含水量的单 独解释率在总解释率中的占比(32. 8%)最大,其次是土壤含水量和土壤pH 的交互作用(12. 1%)以及土壤容重的单独解释率(10. 5%),而土壤pH 的单独解 释率相对较低( 见图 4) .特征与土壤因子偏冗余分析结果Fig.4 Partial redundancy analysis of the T. ramos ss ma community stoichiometrictraits and soil properties3讨论3.1群落水平上荒漠河岸多枝柽柳灌丛TC 、TN 、TP含量及其计量比该研究聚焦于黑河下游极端干旱荒漠河岸地带(年降水量30〜40 mm )沿河梯度上多枝柽柳群落的碳 氮磷化学计量特征及其影响因素.在群落水平上,该研究中多枝柽柳群落TC 含量平均值为380. 27 mg/g,第3期张晓龙等:荒漠河岸多枝柽柳灌丛碳氮磷化学计量特征及其影响因素703略高于黑河下游荒漠河岸地带和中下游戈壁荒漠地区物种水平的TC含量平均值(见表4),而多枝柽柳群落TC含量平均值显著低于黄土高原地区、全球尺度下物种水平的TC含量平均值[27-29].多枝柽柳群落TN含量平均值为30.42mg/g,高于黑河下游荒漠河岸地带和中下游戈壁荒漠地区物种水平的TN含量平均值(见表4),同时也高于黄土高原地区、全球尺度下物种水平的TN含量平均值[27-29].多枝柽柳群落TP含量平均值为1.54mg/g,高于黑河下游荒漠河岸地带物种水平的TP含量平均值(见表4),而略低于中下游戈壁荒漠地区、黄土高原地区、全球尺度下物种水平的TP含量平均值[27-29],这可能是导致该研究中N:P较高的原因.与全球尺度、区域尺度相比较,该研究中多枝柽柳群落具有TC含量低、TN含量高、N:P高、TP含量相对稳定的特点.此外,与黑河下游荒漠河岸地带和黑河中下游荒漠地区物种水平下的研究结果相比,黑河下游荒漠河岸地带群落水平碳氮磷化学计量参数变异系数相对较小(见表4),反映出 多枝柽柳群落水平碳氮磷化学计量特征相对较高的内稳性.表4黑河中下游荒漠地区植物在物种和群落水平下碳氮磷化学计量特征Table4Stoichiometric traits of desert plants in the middle and lower reaches of Heihe at species and community levels,respectively项目黑河下游荒漠河岸地带(群落水平)黑河下游荒漠河岸地带(物种水平)[8]黑河中下游戈壁荒漠地区(物种水平)〔何数值变异系数数值变异系数数值变异系数TC含量/(mg/g)380.27±31.170.08327.29±75.580.23301.22±99.050.33 TN含量/(mg/g)30.42±7.210.2413.88±2.720.2018.81±4.860.26 TP含量/(mg/g) 1.54±0.360.230.58±0.200.34 1.74±0.700.40 C:N12.98±2.290.1824.41±6.820.2815.88±2.680.14 C:P257.09±54.610.21614.94±214.480.35199.68±108.610.54 N:P20.04±3.780.1926.12±6.850.2612.27±5.340.433.2荒漠河岸沿河多枝柽柳群落碳氮磷化学计量变化特征在沿河梯度上,多枝柽柳群落TC含量平均值相对较低,主要与该区域极端干旱和盐碱的环境有关,植物为应对干旱和盐碱胁迫,其自身代谢成本增加,光合速率受到抑制,从而使得多枝柽柳群落的固碳能力降低[31-32],这也可能是多枝柽柳群落TC含量随沿河距离的增加呈显著下降变化趋势的主要原因.由于该地区河流水补给的地下水是植物和土壤的主要水分来源[24],随着沿河距离的增加,地下水埋深逐渐增加,土壤含水量逐渐降低,水分条件变差使得植物生产力下降,多枝柽柳群落TC含量降低[8,17].这和多枝柽柳群落TC含量与土壤含水量呈显著正相关的分析结果相符合,尤其是在土壤水分条件最好的样地T1,群落TC含量平均值为423.67mg/g,而在土壤水分条件最差的样地T9,群落TC含量平均值仅为348.96mg/g,这在一定程度上说明水分条件变化影响着荒漠植物群落碳含量的变化,较低的碳含量可能与极端干旱的环境有关[32].有研究表明,在自然条件下,植物叶片氮含量与土壤氮含量呈线性正相关[33],即使在半干旱-干旱地区的氮添加控制试验中,土壤无机氮含量的增加也会导致植物叶片氮含量的显著增加[34],这与该研究中多枝柽柳群落TN含量与土壤TN含量呈显著正相关的分析结果相符合.该研究中群落相对较高的氮含量主要与优势种多枝柽柳和干旱盐碱生境相关.在沿河梯度上,多枝柽柳是一种典型的内生固氮菌属灌木[35],此外,在盐碱环境下,荒漠植物可积累大量含氮物质,导致多枝柽柳群落具有相对较高的氮含量,相对较高的氮含量可能是荒漠植物对极端干旱和盐碱环境的适应结果[32,36].磷元素被认为是中国陆地植物生长的主要限制性养分,植物磷含量低主要是由土壤磷含量较低引起的[37].该研究中多枝柽柳群落TP含量平均值(1.54 mg/g)略高于全国陆地植物物种平均水平(1.46 mg/g),且与植物吸收关系密切的土壤速效磷含量(4.48mg/kg)也高于全国平均水平(3.83mg/kg)[38],该研究中黑河下游荒漠河岸地带多枝柽柳群落TP 含量可能是由于相对较高的土壤磷含量所致.然而,该研究中多枝柽柳群落TP含量与土壤速效磷含量呈正相关(R=0.353),但不显著,这与该区域盐分胁迫有关.有研究表明,在受盐胁迫土壤中,存在大量的Cl-,SO42-等阴离子,它们会与磷元素产生竞争效应,抑制植物对磷元素的吸收[39],这与该研究中多枝柽柳群落TP含量与土壤电导率呈显著负相关的分析结果相符合.在沿河梯度上,在距河1800~2800m之间,土壤电导率为13.32-15.05mS/cm,极端盐胁迫704环境科学研究第34卷可能抑制植物对磷元素的吸收,这也可能是多枝柽柳群落TP含量呈先下降后上升的变化趋势的主要原因.有研究表明,磷元素主要来源于土壤母质,干旱区降水过程对土壤的淋溶程度较低,相对于氮元素,土壤母质中磷含量相对丰富,使得氮元素更易成为限制性元素[40-41].Gusewell等认为,在群落水平上N:P 更能准确判断植物生长的养分限制[42],而笔者得到的柽柳群落N:P平均值为20.04,相对较高的N:P可能意味着该区域多枝柽柳群落在生长旺季氮过量而磷含量相对不足.3.3荒漠河岸沿河多枝柽柳群落碳氮磷化学计量格局形成的影响因素分析在干旱区,尤其是极端干旱地区,水分条件是影响植物生长和分布的主要影响因子[17].该研究中多枝柽柳群落TC、TN、TP含量均与土壤含水量呈显著正相关,在黑河下游荒漠河岸地带,水分条件较好的近河地带,土壤水分和土壤养分含量相对较高,植物群落生长条件较好,植物群落通过水分-养分的耦合效应获取更多的养分[8,43];随着沿河垂直距离的增加,养分和水分条件变差,导致植物能获取的养分减少,使得植物TC、TN、TP含量显著降低[8].偏冗余分析结果表明,土壤含水量、土壤容重和土壤pH会对多枝柽柳群落碳氮磷化学计量特征产生显著影响,进一步说明多枝柽柳群落TC、TN、TP含量与水分条件有关.水分条件较土壤pH的影响作用更为明显,可能是因为黑河下游极端干旱的环境导致水分条件更易成为荒漠植物生长的限制因素.此外,土壤含水量和土壤pH的交互作用解释了多枝柽柳群落碳氮磷化学计量特征变化的12.1%,表明该区域土壤盐碱共同影响着多枝柽柳群落的生长.考虑到植被与环境之间的复杂关系,在黑河下游荒漠河岸地带进行长期多尺度野外调查,或者控制试验可能更有利于进一步阐明多枝柽柳群落对土壤水盐和养分的响应.4结论a)黑河下游荒漠河岸地带多枝柽柳群落具有TC含量低、TN含量高、N:P高、TP含量相对稳定的特点.与黑河中下游地区荒漠植物物种水平相比,在群落水平上,荒漠河岸多枝柽柳灌丛碳氮磷化学计量特征的变异系数相对较小,内稳性较强.群落水平N:P的分析表明,黑河下游荒漠河岸多枝柽柳群落在生长旺季受磷元素的限制程度较大.b)在沿河梯度上,多枝柽柳群落TC、TN、TP的含量以及C:N、C:P和N:P在不同沿河距离样地内均具有显著差异(P<0.05).随着沿河距离的增加,多枝柽柳群落TC、TN、TP含量和C:N:P均呈现出显著的变化趋势.土壤含水量、土壤容重和土壤pH较好地解释了多枝柽柳群落碳氮磷化学计量特征的变化,共同解释了总变异的57.7%.c)在解释多枝柽柳群落碳氮磷化学计量特征的变化方面,土壤含水量以及土壤含水量和土壤pH交互作用的贡献率大于土壤pH,表明水分是该区域植物生长的主要限制因子,植物可能通过调节自身营养元素的比例来适应极端干旱盐碱的环境.参考文献(References):[1]ELSER J J,STERNER R,GOROKHOVA E,et aZ.Biologicalstoichiometry from genes to ecosystems[J].Ecology Letters,2000,3:540-550.[2]田地,严正兵,方精云•植物化学计量学:一个方兴未艾的生态学研究方向[J].自然杂志,2018,40(4):235-242.TIAN Di,YAN Zhengbing,FANG Jingyun.Plant stoichiometry:aresearch frontier in ecology[J].Chinese Journal of Nature,2018,40(4):235-242.[3]TANG Z Y,XL W T,ZHOL G Y,et aZ.Patterns of plant carbon,nitrogen,and phosphorus concentration in relation to productivity inChina's terrestrial ecosystems[J].Proceedings of the NationalAcademy of Sciences of the Lnited States of America,2018,115:4033-4038.[4]DL E Z,TERRER C,PELLEGRINI A,et aZ.Global patterns ofterrestrial nitrogen and phosphorus limitation[J].NatureGeoscience,2020,13:221-226.[5]ELESER J J,ACHARYA K,KYLE M,et aZ.Growth rate­stoichiometry couplings in diverse biota[J].Ecology Letters,2003,6(10):936-943.[6]HAN W X,FANG J Y,REICH P B,et aZ.Biogeography andvariability of eleven mineral elements in plant leaves acrossgradients of climate,soil and plant functional 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Influence of Purity Degree on the Evolution the Me

Influence of Purity Degree on the Evolution the Me

J. Chem. Chem. Eng. 6 (2012) 920-924Influence of Purity Degree on the Evolution the Mechanical Properties of Aluminium CommercialAhmed Hakem* and Y. BouafiaLaboratory LaMoMS, Mouloud MAMMERI University of Tizi-Ouzou Hasnaoua II, 15000 AlgeriaReceived: July 30, 2012 / Accepted: August 28, 2012 / Published: October 25, 2012.Abstract: The influence of the purity degree of the commercial aluminium on the mechanical properties: elastic stress, tensile strength, Brinell hardness, resilience and elongation at break was investigated. It was found that the first three resistance characteristics decrease with the growth of the purity of the material chosen to the detriment of two ductility characteristics that rise to the three states considered: crude of casting noted: F, Annealed noted: O, hardened noted : H1/4. Furthermore, it is important to note that the hardened and the annealed lead respectively to a considerable hardening and a considerable softening. This hardening and this softening of the material in question can be respectively associated with the increase in dislocation density and immigration impurity elements of dislocations.Key words: Purity, aluminum, properties, mechanical, hardness.1. IntroductionThe natural aluminum does not exist. Indeed, although it equals to 8% of elements on earth, man invented it by extracting it from bauxite. The discovery of aluminum material with outstanding features: light weight, ductility, mechanical strength and weather, fastness, good thermal and electrical conductivities. These properties have quickly made aluminum one of the most magical materials used inthe production of consumer goods of high and very high series with a tendency to consolidate its positionas second only to steel. Extracted for the first time inthe laboratory in 1825 and operated only industrially since 1880 after the discovery of electrolysis, aluminum has become in a century for its strength and lightness in a wide range of applications on land, sea and air. This material has no harmful influence on environment both in production and in its recovery toits recyclability.*Corresponding author:Ahmed Hakem, Doctorand/Magister, research field:aluminium alloys. E-mail:********************.Aluminium and its alloys have a positive impact onquality of life for all of us.Historically, the physical, chemical and mechanicalstudy of aluminum business raised many questions ofscientific interest and technological importance whichdid not leave indifference to many researchers, sincethis material is widely used in industry and in practice.It easily lends itself to shaping the cold plasticdeformation (drawing, spinning, bending, cutting andboiler). It demonstrated excellent performance in ahumid atmosphere and ocean.Since the commercial aluminum enters thecomposition of many achievements and industrialapplications, which are subject to various mechanicalstresses, and in order to achieve a reliable product thatmust meet the proper functioning of the system towhich it belongs, the properties of this mechanicalmaterial saw multitudes of investigations and attractedthe attention of many researchers. It was shown thatthe purity of the commercial aluminum significantlyinfluences its mechanical properties.In the literature, it was shown that the value of the l Rights Reserved.Influence of Purity Degree on the Evolution the Mechanical Properties of Aluminium Commercial921yield strength of pure polycrystalline aluminum is about 4 times lower than that of the commercial aluminum.Many authors have studied the mechanical properties of commercial aluminum with a purity of at least 99%. They lead to the following results: in the annealed condition, the majority of the mechanical properties are low, but they can be improved by cold working, for example, in the annealed condition hardened state, the yield increased from 28 to 125 MPa and the tensile strength varies from 70 to 130 MPa.However, the results obtained by different authors are often conflicting and tight, if not contradictory. Our job is to contribute to the effect of purity on the mechanical strength, Brinell hardness and resilience of the aluminum used in several commercial industrial achievements [1-11].2. MaterialThe materials used are provided by the national electro-industries. There are three types of aluminum commercial purity (Al-99, 0%, Al-99, 5%, Al-99, 8%) which were selected to carry out this study.3. Elaboration of the Alloy3.1 CastingThe melting of the metal in a gas oven production will switch from front to back, with a graphite crucible with a capacity of 350 Kg load composed approximately 100% of aluminum ingots new commercial dimensions standardized composition and specified characteristics, delivered by the French company Pechiney. The mass has become liquid full at about 700 °C. The liquid mass is then subjected to degassing treatment and coverage in the oven.Then the metal is poured, or in a warm pocket of 50 Kg prepared for this purpose for sand casting and series, or in a holding furnace of 150 kg set properly for the unit shell mold preheated and that we proceed carefully prepared refining operations. Parts can be cast into the shell, respectively single metal or sand molds prepared for it, so the reference specimens are known as a crude of casting noting: F. To seek to increase over the characteristics of resistance to the state F, the two materials with different degrees of purity will be subject to specific treatments of annealed and the hardened.3.2 MoldingMETAL SHELL: In this mode of molding, the mold consists of two steel slabs (5% chromium), which are responsible for maintaining the footprints. These steel slabs, separated by a parting line, may be prepared and heated to a temperature of 200-300 °C. After molding, the specimens cast metal shell by gravitation will be divided into three lots, each consisting of five identical tensile specimens, five specimens of resilience and a sample for the micrographic observation considering three states: a crude of casting notes:F, annealing noted:O and hardened noted: H1/4.3.3 Treatments•Annealing: heating and dissolved with homogenization at 540 °C for 10 h followed by cooling in the oven;•Hardening: deformation of 25% in 3 passes with a six-cylinder mill.Once processing is done, the material will be testedin quasi-static uniaxial tensile loads and low speeds, Brinell hardness and quasi dynamic resilience to quantify the different characteristics of resistance and ductility needed for different calculations which we need the design engineer at the department. The microstructure complement the study to fully identify the material.4. Experimental ProcedureTo determine the behavior of the material to meet the different demands it may encounter during use, these solicitations are reproduced using static or dynamic tests, usually performed on standardl Rights Reserved.Influ922specimens t material. Fo identify the HB for the s the mode resistance a We will des main mecha obtained in t 5. Results The avera strength an aluminum c five identic cases and ar 5.1 Influenc Caracteristi Commercial For the commercial variations o average str average stresFig. 1 Grou degree) of com specimens of crude of casti noted: H1/4. uence of Puri to determine ur techniques various con stress field, K of fracture,and metallog scribe in mo anical charact this study.and Discus age values of nd hardness commercial a al specimens re represented ce of Purity D cs of Resista l Aluminumthree state aluminum, w of the three ess of elasti ss noted <σm >up of graphs (a mparison in av the aluminum ing noted: F, a ity Degree on the characte s are used, na nstraints, the Kcv resilience , fragility a graphy to ide ore detail an teristics of th ssionf mechanical of the thre are those giv s for each o d in Figs. 1-5.Degree on th nce of the Th es considere we followed main featureicity noted <> and Brinell average stress veraging a ser m commercial o annealing noted n the Evolutio eristics encry amely: the pu Brinell hard e telling us ab and the im entify structu nd present in he material b strength, im ee states of ven by avera of the respec . he Evolution hree States of ed in choo the evolutio es of resista <σe >, maxim hardness aver of elasticity-pu ies of five iden of the three st d: O and hard on the Mecha yptedull to dness bout mpact ures. n the eing mpact the ging ctive n the f the osing n ofance: mum rageurity nticaltates:denedFig.degr spec crud noteFig.aver of fi the O annote stud F mec stat the spe mec W cha nical Propert . 2 Group of ree) of compar cimens of the a de of casting n ed: H1/4.. 3 Group rage-purity de five identical sp three states: c nd hardened n ed <HB > dep died.Figs. 1-3 show chanical char tes are consid purity at thed of decreas chanical char We also note aracteristics o ties of Alumin f graphs (max rison in averag aluminum com noted: F, annea p of graph egree) of comp pecimens of th crude of castin noted: H1/4.pending on t w that the av racteristics o dered to decr he expense o se varies diff racteristic and that the ave of resistance nium Comme ximum average ging a series of mmercial of th aling noted: O s (hardness parison in aver he aluminum c g noted: F, ann the purity of verage curves of resistance rease with th of ductility, h ferently depe d the state con erage curves of the harden erciale stress-purityf five identical he three states:and hardened Brinell HB raging a series commercial of nealing noted:f the material s of the three of the three he growth of however, the ending on the nsidered. of the three ned state arey l : dBs f : l e e fe e e el Rights Reserved.InfluFig. 4 Grou degree) of com specimens of crude of casti noted: H1/4.Fig. 5 Grou degree) of com specimens of crude of casti noted: H1/4.located too which are ju 5.2 Influenc Caracteristi Commercial The same commercial evolution o uence of Puri up of graphs mparison in av the aluminum ing noted: F, a up of graphs mparison in av the aluminum ing noted: F, a far above tho ust above thos ce of Purity D cs of Ductili l Aluminum for the three aluminum, of variations ity Degree on (average elon veraging a ser m commercial o annealing noted (average res veraging a ser m commercial o annealing noted ose of the ann se of the as-ca Degree on th ity of the Th e states consid we have al s of two m n the Evolutio ngation A %-pu ies of five iden of the three st d: O and hard silience Kcv -pu ies of five iden of the three st d: O and hard nealed condit ast state. he Evolution ree States of dered in choo lso followed main features on the Mecha uritynticaltates:deneduritynticaltates:denedtion,n the f the osing the s ofduc ave the F two stat pur how dep stat W cha loca are 6. C In Brin com stra disl also plas the that dur mat matpres lead Re [1][2][3][4]nical Propert ctility: averag erage elongat purity of the Figs. 4 and 5o mechanical tes are consid ity at the e wever, the pending on th te considered We also note aracteristics o ated too far a themselves ju Conclusion n this study,nell hardnes mmercial wer ain hardening locations, but o leads to a c sticity simult material har t of the mate ing this ann terial. The terial in the a sence of het ds to softenin ferencesLakhtine. Me 3rd ed., 1982Solidification Volume 2: Fo Hakem, A.; B Processes of Characteristic Alloy Hypo Advanced P Petersburg, R Hakem A.;Influence of t ties of Alumin ge resilience tion designat material stud 5 show that t characteristic dered to grow expense of r growth sp he mechanic e that the av of ductility o above those o ust above tho nthe mechan ss and resil re studied. W g delays the o t accelerates t considerable taneously. In rdens, but the rial in the ha nealing is a poor mecha as-cast state terogeneities.ng of the mate etallography an 2. ns characteris oundry alloys, A Bouafia, Y.; Sa f Molding and cs of Resistanc oeutectic Asi7Problems in M Russia, July 1-5Benmedjber, the Addition of nium Comme e designated ted <A%> d died. the average c cs of ductility w with the g resistance ch peed varies cal characteri verage curves of the annea of the as-cast ose of the har ical propertie ience of th We have sho onset of the m the process o hardening an n the anneale e hardening i ardened state a great plast anical proper were associa . The increa erial. nd Heat Treatm tics of alum Amer Foundry alhi, A. Influenc Time of Mat ce of Ductility 7mg, Summe Mechanics AP , 2010.A.; Salhi, A.f Mg, the Mode ercial923<Kcv> and depending on curves of the y of the three growth of the haracteristics,differently istic and the s of the two led state are t state, which dened state.es of tensile,e aluminum own that the movement of f rupture and nd a drop of ed condition,is lower than . In addition,ticity of the rties of the ated with the ase in purity ment of Metals;minum alloys:society, 1993.ce of Industrial turation on the and Structural er School in PM’ 2010, St.; Bouafia, Y.e of Elaboration 3dn e e e , y e o eh , m e f d f , n , e e e y; : l e l n . . nl Rights Reserved.Influence of Purity Degree on the Evolution the Mechanical Properties of Aluminium Commercial 924and the Time of Maturation on the Mechanical andStructural Properties of the Alloy Eutectic 44000Unstandardized, International Summer School-Conference Advanced Problems in MechanicsAPM 2011, St. Petersburg Russia, July 1-5, 2011.[5]Bäckerud L. Solidification Characteristics of AluminumAlloy; Oslo: Norway, 1986-1996..[6]Hakem, A.; Bouafia, Y.; Salhi, A. Influence of UserDevelopment and Aging on Mechanical Characteristicsand Microstructure of the Alloy Foundry AlSi10Mg,ACMA 2010, Marrakech, Marocco, May 12-14,2010.[7]Hakem, A.; Bouafia, Y.; Naïli, S.; Bouhaci, A.Development of Industrial Aluminum Alloys FoundryAlSi7Mg, AlSi10Mg and AlSi13Mg, International Symposium-Characterization and Modeling of Materials and Structures, University Mouloud Mammeri Tizi-Ouzou, Algeria, November 16-18, 2008.[8]Hakem, A. Memory Magister, Microstructure andMechanical Properties of Alloy hypoeutectic Al7SiMg,Department of Engineering-Mechanical Engineering,Faculty of Engineering Building, University MouloudMammeri Tizi-Ouzou Algeria, 2005.[9]Colombia, M.; Coll. Industrial Materials: MetalMaterials; Dunod: Paris, 2000; p 867.[10]Jean-Paul, B.; Jean-Marie, D. Materials; EcolePolytechnique de Montreal: Montreal, 2000; p 729.[11]Jean, B. G. M. Handbook of Metallurgy: Preparation,Structure, Properties, Normalization; 1ereédition,AFNOR-Nathan: Paris, 1997; p 232.l Rights Reserved.。

沙子吸附铅

沙子吸附铅

Journal of Hazardous Materials B137(2006)384–395Removal of copper(II)and lead(II)from aqueoussolution by manganese oxide coated sand I.Characterization and kinetic studyRunping Han a ,∗,Weihua Zou a ,Zongpei Zhang a ,Jie Shi a ,Jiujun Yang baDepartment of Chemistry,Zhengzhou University,No.75of Daxue North Road,Zhengzhou 450052,PR ChinabCollege of Material Science and Engineering,Zhengzhou University,No.75of Daxue North Road,Zhengzhou 450052,PR ChinaReceived 8November 2005;received in revised form 25December 2005;accepted 13February 2006Available online 28February 2006AbstractThe preparation,characterization,and sorption properties for Cu(II)and Pb(II)of manganese oxide coated sand (MOCS)were investigated.A scanning electron microscope (SEM),X-ray diffraction spectrum (XRD)and BET analyses were used to observe the surface properties of the coated layer.An energy dispersive analysis of X-ray (EDAX)and X-ray photoelectron spectroscopy (XPS)were used for characterizing metal adsorption sites on the surface of MOCS.The quantity of manganese on MOCS was determined by means of acid digestion analysis.The adsorption experiments were carried out as a function of solution pH,adsorbent dose,ionic strength,contact time and temperature.Binding of Cu(II)and Pb(II)ions with MOCS was highly pH dependent with an increase in the extent of adsorption with the pH of the media inves-tigated.After the Cu(II)and Pb(II)adsorption by MOCS,the pH in solution was decreased.Cu(II)and Pb(II)uptake were found to increase with the temperature.Further,the removal efficiency of Cu(II)and Pb(II)increased with increasing adsorbent dose and decreased with ionic strength.The pseudo-first-order kinetic model,pseudo-second-order kinetic model,intraparticle diffusion model and Elovich equation model were used to describe the kinetic data and the data constants were evaluated.The pseudo-second-order model was the best choice among all the kinetic models to describe the adsorption behavior of Cu(II)and Pb(II)onto MOCS,suggesting that the adsorption mechanism might be a chemisorption process.The activation energy of adsorption (E a )was determined as Cu(II)4.98kJ mol −1and Pb(II)2.10kJ mol −1,respectively.The low value of E a shows that Cu(II)and Pb(II)adsorption process by MOCS may involve a non-activated chemical adsorption and a physical sorption.©2006Elsevier B.V .All rights reserved.Keywords:Manganese oxide coated sand (MOCS);Cu(II);Pb(II);Adsorption kinetic1.IntroductionThe presence ofheavy metals in the aquatic environment is a major concern due to their extreme toxicity towards aquatic life,human beings,and the environment.Heavy metal ions from wastewaters are commonly removed by chemical precipitation,ion-exchange,reverse osmosis processes,and adsorption by activated carbon.Over the last few decades,adsorption has gained importance as an effective purification and separation technique used in wastewater treatment,and the removal of heavy metals from metal-laden tap or wastewater∗Corresponding author.Tel.:+8637167763707;fax:+8637167763220.E-mail address:rphan67@ (R.Han).is considered an important application of adsorption processes using a suitable adsorbent [1,2].In recent years,many researchers have applied metal oxides to adsorption of heavy metals from metal-laden tap or wastewa-ter [3].Adsorption can remove metals over a wider pH range and lower concentrations than precipitation [4].Iron,aluminum,and manganese oxides are typically thought to be the most important scavengers of heavy metals in aqueous solution or wastewater due to their relatively high surface area,microporous structure,and possess OH functional groups capable of reacting with met-als,phosphate and other specifically sorbing ions [5].However,most metal oxides are available only as fine powders or are gener-ated in aqueous suspension as hydroxide floc or gel.Under such conditions,solid/liquid separation is fairly difficult.In addition,metal oxides along are not suitable as a filter medium because of0304-3894/$–see front matter ©2006Elsevier B.V .All rights reserved.doi:10.1016/j.jhazmat.2006.02.021R.Han et al./Journal of Hazardous Materials B137(2006)384–395385their low hydraulic conductivity.Recently,several researchers have developed techniques for coating metal oxides onto the surface of sand to overcome the problem of using metal oxides powers in water treatment.Many reports have shown the impor-tance of these surface coatings in controlling metal distribution in soils and sediments[3,6,7].In recent years,coated minerals have been studied because of their potential application as effective sorbents[3,8,9].Iron oxide coated meterials for heavy metal removal have been proved successful for the enhancement of treatment capacity and efficiency when compared with uncoatedfilter media,such as sil-ica sand[10–14],granular activated carbon[15]and polymeric media[16,17].For example,Edwards and Benjamin[7]found that coated media have similar properties to unattached coating materials in removing metals over a wide pH range,and that Fe oxide coated sand was more effective than uncoated sand.Bai-ley et al.[18]used iron oxide coated sand to remove hexavalent chromium from a synthetic waste stream.The influent contained 20mg l−1Cr(VI)and better than99%removal was achieved. Satpathi and Chaudhuri[19]and Viraraghavan et al.[20]have recently reported on the ability of this medium to adsorb metals from electroplating rinse waters and arsenic from drinking water sources,respectively.Green-Pedersen and Pind reported that a ferrihydrite-coated montmorillonite surface had a larger specific surface area and an increased sorption capacity for Ni(II)com-pared to the pure systems[21].Meng and Letterman[22]found that the adsorption properties of oxide mixtures are determined by the relative amount of the components.They also found that ion adsorption on aluminum oxide-coated silica was better mod-eled assuming uniform coverage of the oxide rather than using two distinct surfaces[23].Lo and Chen[8]determined the effect of Al oxide mineralogy,amount of oxide coating,and acid-and alkali-resistance on the removal of selenium from water.Bran-dao and Galembecket reported that the impregnation of cellulose acetates with manganese dioxide resulted in high removal effi-cient of Cu(II),Pb(II),and Zn(II)from aqueous solutions[24]. Al-Degs and Khraisheh[25]also reported that diatomite and manganese oxide modified diatomite are effective adsorbents for removing Pb2+,Cu2+,and Cd2+ions.The sorption capac-ity of Mn-diatomite was considerably increased compared to the original material for removing the studied metals.Filtration quality of diatomite is significantly increased after modification with Mn-oxides.Merkle et al.[26–28]reported that manganese dioxide coated sand was effective for removal of arsenic from ground water in column experiments.Merkle et al.developed a manganese oxide coating method on anthracite to improve the removal of Mn2+from drinking water and hazardous waste effluent.They generated afilter media with an increased surface area after coating with manganese oxides and found manganese oxide coated media have the ability to adsorb and coprecipi-tate a variety of inorganic species.Stahl and James[29]found their manganese oxide coated sands generated a larger surface area and increased adsorption capability with increasing pH as compared to uncoated silica sand.Additional researchers have been investigated to evalu-ate coating characteristics.X-ray diffraction(XRD),X-ray photoelectron spectroscopy(XPS),Fourier transform infrared spectroscopy(FTIR),transmission electron microscopy(TEM), and scanning electron microscopy(SEM)have been used as well to identify components,distribution,and structure of surface oxide coating[7,9,30,31].An energy dispersive X-ray (EDAX)technique of analysis has been used to characterize metal adsorption sites on the sorbent surface.Typically,oxide was non-uniform over the surface as both the oxide and substratum had been observed[7].The research described here was designed to investigate characteristics of manganese oxide coated sand(MOCS)and test the properties of MOCS as an adsorbent for removing copper(II)and lead(II)from synthetic solutions in batch system.SEM/EDAX,XRD,XPS and BET analysis were employed to examine the properties of adsorption reactions for Cu(II)and Pb(II)ions on MOCS in water.The system variables studied include pH,MOCS dose,ionic strength,contact time and temperature.The kinetic parameters,such as E a,k1,k2, have been calculated to determine rate constants and adsorption mechanism.1.1.Kinetic parameters of adsorptionThe models of adsorption kinetics were correlated with the solution uptake rate,hence these models are important in water treatment process design.In order to analyze the adsorption kinetics of MOCS,four kinetic models including the pseudo-first-order equation[32],the pseudo-second-order equation[33], Elovich equation[34],and intraparticle diffusion model[35] were applied to experimental data obtained from batch metal removal experiments.A pseudo-first-order kinetic model of Lagergen is given as log(q e−q t)=log q e−K1t2.303(1)A pseudo-second-order kinetic model istq t=1(K2q2e)+tq e(2) andh=K2q2e(3) an intraparticle diffusion model isq t=K t t1/2+C(4) and an Elovich equation model is shown asq t=ln(αβ)β+ln tβ(5) where q e and q t are the amount of solute adsorbed per unit adsorbent at equilibrium and any time,respectively(mmol g−1), k1the pseudo-first-order rate constant for the adsorption process (min−1),k2the rate constant of pseudo-second-order adsorption (g mmol−1min−1),K t the intraparticle diffusion rate constant (mmol g−1min−1),h the initial sorption rate of pseudo-second-order adsorption(mmol g−1min−1),C the intercept,αthe initial sorption rate of Elovich equation(mmol g−1min−1),and386R.Han et al./Journal of Hazardous Materials B137(2006)384–395the parameter βis related to the extent of surface coverage and activation energy for chemisorption (g mmol −1).A straight line of log(q e −q t )versus t ,t /q t versus t ,q t versus ln t ,or q t versus t 1/2suggests the applicability of this kinetic model and kinetic parameters can be determined from the slope and intercept of the plot.1.2.Determination of thermodynamic parametersThe activation energy for metal ions adsorption was calcu-lated by the Arrhenius equation [36]:k =k 0exp −E aRT (6)where k 0is the temperature independent factor ing mmol −1min −1,E a the activation energy of the reaction of adsorption in kJ mol −1,R the gas constant (8.314J mol −1K −1)and T is the adsorption absolute temperature (K).The linear form is:ln k =−E aRT+ln k 0(7)when ln k is plotted versus 1/T ,a straight line with slope –E a /R is obtained.2.Materials and methods 2.1.AdsorbentThe quartz sand was provided from Zhengzhou’s Company of tap water in China.The diameter of the sand was ranged in size from 0.99to 0.67mm.The sand was soaked in 0.1mol l −1hydrochloric acid solution for 24h,rinsed with distilled water and dried at 373K in the oven in preparation for surface coating.Manganese oxide coated sand was accomplished by utilizing a reductive procedure modified to precipitate colloids of man-ganese oxide on the media surface.A boiling solution containing potassium permanganate was poured over dried sand placed in a beaker,and hydrochloric acid (37.5%,W HCl /W H 2O )solution was added dropwise into the solution.After stirring for 1h,the media was filtered,washed to pH 7.0using distilled water,dried at room temperature,and stored in polypropylene bottle for future use.2.2.Metal solutionsAll chemicals and reagents used for experiments and anal-yses were of analytical grade.Stock solutions of 2000mg l −1Pb(II)and Cu(II)were prepared from Cu(NO 3)2and Pb(NO 3)2in distilled,deionized water containing a few drops of concen-trated HNO 3to prevent the precipitation of Cu(II)and Pb(II)by hydrolysis.The initial pH of the working solution was adjusted by addition of HNO 3or NaOH solution.2.3.Mineral identificationThe mineralogy of the sample was characterized by X-ray diffraction (XRD)(Tokyo Shibaura Model ADG-01E).Pho-tomicrography of the exterior surface of uncoated sand and man-ganese oxide coated sand was obtained by SEM (JEOL6335F-SEM,Japan).The distribution of elemental concentrations for the solid sample can be analyzed using the mapping analysis of SEM/EDAX (JEOL SEM (JSM-6301)/OXFORD EDX,Japan).The existence of Cu(II)and Pb(II)ions on the surface of manganese oxide coated sand was also confirmed by using EDAX.Samples for EDAX analysis were coated with thin carbon film in order to avoid the influence of any charge effect during the SEM operation.The samples of MOCS and MOCS adsorbed with copper/lead ions were also analyzed by X-ray photoelectron spectroscopy (XPS)(ESCA3600Shimduz).2.4.Specific surface area and pore size distribution analysesAnalyses of physical characteristics of MOCS included spe-cific surface area,and pore size distributions.The specific sur-face area of MOCS and pore volumes were test using the nitrogen adsorption method with NOV A 1000High-Speed,Automated Surface Area and Pore Size Analyer (Quantachrome Corpora-tion,America)at 77K,and the BET adsorption model was used in the calculation.Calculation of pore size followed the method of BJH according to implemented software routines.2.5.Methods of adsorption studiesBatch adsorption studies were conducted by shaking the flasks at 120rpm for a period of time using a water bath cum mechanical shaker.Following a systematic work on the sorp-tion uptake capacity of Cu(II)and Pb(II)in batch systems were studied in the present work.The experimental process was as following:put a certain quantity of MOCS into conical flasks,then,added the solute of metals of copper or lead in single component system,vibrated sometime at a constant speed of 120rpm in a shaking water bath,when reached the sorption equilibrium after 180min,took out the conical flasks,filtrated to separate MOCS and the solution.No other solutions were provided for additional ionic strength expect for the effect of ionic strength.The concentration of the free metal ions in the filtrate was analyzed using flame atomic absorption spectrometer (AAS)(Aanalyst 300,Perkin Elmer).The uptake of the metal ions was calculated by the difference in their initial and final concentrations.Effect of pH (1.4–6.5),quantity of MOCS,contact time,temperature (288–318K)was studied.The pH of the solutions at the beginning and end of experiments was measured.Each experiment was repeated three times and the results given were the average values.2.5.1.Effect of contact time and temperature on Cu(II)and Pb(II)adsorptionA 2.0g l −1sample of MOCS was added to each 20ml of Cu(II)or Pb(II)solutions with initial concentration of Cu(II)0.315mmol l −1and Pb(II)0.579mmol l −1,respectively.The temperature was controlled with a water bath at the temperature ranged from 294to 318K for the studies.Adsorbent of MOCS and metal solution were separated at pre-determined time inter-R.Han et al./Journal of Hazardous Materials B137(2006)384–395387 vals,filtered and analyzed for residual Cu(II)and Pb(II)ionconcentrations.2.5.2.Effect of pH on the sorption of Cu(II)and Pb(II)byMOCSThe effect of pH on the adsorption capacity of MOCSwas investigated using solutions of0.157mmol l−1Cu(II)and0.393mmol l−1Pb(II)for a pH range of1.4–6.5at293K.A20g l−1of MOCS was added to20ml of Cu(II)and Pb(II)solu-tions.Experiments could not be performed at higher pH valuesdue to low solubility of metal ions.2.5.3.Effect of MOCS doseIt was tested by the addition of sodium nitrate and calciumnitrate to the solution of Cu(II)and Pb(II),respectively.The doseof adsorbents were varied from10to80g l−1keeping initial con-centration of copper0.157mmol l−1and lead0.393mmol l−1,respectively,and contact time was180min at the temperature of293K.2.5.4.Effect of ionic strength on Cu(II)and Pb(II)adsorptionThe concentration of NaNO3and Ca(NO3)2used rangedfrom0to0.2mol l−1.The dose of adsorbents were20g l−1,the initial concentration of copper0.157mmol l−1and lead0.393mmol l−1,respectively,and contact time was180min atthe temperature of293K.The data obtained in batch model studies was used to calculatethe equilibrium metal uptake capacity.It was calculated for eachsample of copper by using the following expression:q t=v(C0−C t)m(8)where q t is the amount of metal ions adsorbed on the MOCS at time t(mmol g−1),C0and C t the initial and liquid-phase concentrations of metal ions at time t(mmol l−1),v the volume of the aqueous phase(l)and m is the dry weight of the adsorbent(g).3.Results and discussion3.1.Mineralogy of manganese oxide coated sandThe samples of sand coated with manganese oxide were dark colored(brown–black)precipitates,indicating the presence of manganese in the form of insoluble oxides.The X-ray diffrac-tion spectrum(XRD)of the samples(data not shown)revealed that the manganese oxide were totally amorphous,as there was not any peak detected,indicative of a specific crystalline phase. SEM photographs in Fig.1were taken at10,000×magnifi-cations to observe the surface morphology of uncoated sand and manganese oxide coated sand,respectively.SEM images of acid-washed uncoated quartz sand in Fig.1(a)showed very ordered silica crystals at the surface.The virgin sand had a rela-tively uniform and smooth surface and small cracks,micropores or light roughness could be found on the sand -paring the images of virgin(Fig.1(a))and manganeseoxide Fig.1.SEM micrograph of sample:(a)sand;(b)manganese oxide coated sand. coated sand(Fig.1(b)),MOCS had a significantly rougher sur-face than plain sand and the coated sand surfaces were apparently occupied by newborn manganese oxides,which were formed during the coating process.Fig.1(b)also showed manganese oxides,formed in clusters,apparently on occupied surfaces.At the micron scale,the synthetic coating was composed of small particles on top of a more consolidated coating.In most regions individual particles of manganese oxide(diameter=2–3␮m) appeared to be growing in clumps in surface depressions and coating cracks.The amount of manganese on the surface of the MOCS,measured through acid digestion analysis,was approx-imately5.46mg Mn/g-sand.3.2.SEM/EDAX analysisThe elements indicated as being associated with manganese oxide coated were detected by the energy dispersive X-ray spec-trometer system(EDAX)using a standardless qualitative EDAX analytical technique.The peak heights in the EDAX spectra are proportional to the metallic elements concentration.The quali-tative EDAX spectra for MOCS(Fig.2(a))indicated that Mn,O,388R.Han et al./Journal of Hazardous Materials B137(2006)384–395Fig.2.EDAX spectrum of MOCS under:(a)adsorbed without copper and lead ion;(b)adsorbed copper ions;(c)adsorbed lead ions.Si,and K are the main constituents.These had been known as the principal elements of MOCS.EDAX analysis yielded indirect evidence for the mechanism of manganese oxide on the surface of MOCS.The peak of Si occurred in EDAX showed that man-ganese oxides do not covered a full surface of the MOCS.If the solid sample of MOCS caused a change of elemental con-stitution through adsorption reaction,it could be inferred that manganese oxide has already brought about chemical interac-tion with adsorbate.The EDAX spectrum for copper and lead system was illustrated in Fig.2(b and c).It could be seen that copper and lead ion became one element of solid sample in this spectrum.The reason was that copper and lead ions were chemisorbed on the surface of MOCS.Dot mapping can provide an indication of the qualitative abundance of mapping elements.The elemental distribution mapping of EDAX for the sample of MOCS and MOCS adsorbed copper or lead ions is illustrated in Fig.3.The bright points represented the single of the element from the solid sam-ple.A laryer of manganese oxide coating is clearly shown in the dot map for Mn in Fig.3(a),and a high density of white dots indicates manganese is the most abundant element.Results indicated that manganese oxide was spread over the surface of MOCS,and was a constituent part of the solid sample.The ele-ment distribution mapping of EDAX for the sample ofMOCS Fig.3.EDAX results of MOCS(white images in mapping represent the cor-responding element):(a)adsorbed without copper and lead ion;(b)adsorbed copper ions;(c)adsorbed lead ions.R.Han et al./Journal of Hazardous Materials B137(2006)384–395389Fig.4.XPS wide scan of the manganese oxide coated sand. reacting with copper and lead ions is illustrated in Fig.3(b and c).Copper or lead ions were spread over the surfaces of MOCS. Results indicated that manganese oxide produces chemical bond with copper or lead ions.Thus,copper or lead element was a constituent part of the solid sample.3.3.Surface characterization using the X-ray photoelectron spectroscopy(XPS)XPS analyses were performed on samples of MOCS alone and reacting with copper or lead ions.The wide scan of MOCS is presented in Fig.4.It can be noticed that the major elements constituent are manganese,oxygen,and silicon.Detailed spectra of the peaks are shown in Fig.5.Manganese oxides are generally expressed with the chemical formula of MnO x,due to the multiple valence states exhibited by Mn.Therefore,it is reasonable to measure the average oxidation state for a manganese mineral[37].The observation of the Mn 2p3/2peak at641.9eV and the separation between this and the Mn2p1/2peak of11.4eV indicates the manganese exhibited oxidation between Mn3+and Mn4+as shown from the auger plot,but it can be seen to show Mn4+predominantly from the Mn2p3/2peaks[38].The large peak in Fig.5(b)is a sum of the two peaks at 529.3and533.1eV,which can be assigned to O1s;a low bind-ing energy at529.7eV,which is generally accepted as lattice oxygen in the form of O2−(metal oxygen bond).This peak is characteristic of the oxygen in manganese oxides.The second peak at533.4eV can be assigned to surface adsorbed oxygen in the form of OH−[38].As seen the XPS spectra of the sample of MOCS reacting with copper,Fig.6(a)shows the binding energies of the observed photoelectron peaks of Cu2p3/2,2p1/2.The binding energy of the Cu2p3/2peak at a value of933.9eV shows the presence of copper(+2).The XPS spectra obtained after Pb(II)adsorption on MOCS is presented in Fig.6(b).Fig.6(b)shows that doublets charac-teristic of lead appear,respectively,at138.3eV(assigned to Pb 4f7/2)and at143.8eV(assigned to Pb4f5/2)after loadingMOCSFig.5.XPS detailed spectra of MOCS:(a)Mn2p3/2;(b)O1s.with Pb(II)solution.The peak observed at138.3eV agrees with the138.0eV value reported for PbO[39].This shows afixation of lead onto MOCS during the process.3.4.Specific surface area and pore size distribution analysesThe specific surface areas for sand and MOCS under un/adsorbed Pb(II)ions are summarized in Table1.Plain uncoated sand had a surface area of0.674m2g−1.A surface coating of manganese oxide increased the surface area of sand to0.712m2g−1,while average pore diameter decreased from 51.42to42.77˚A.This may be caused by the increase in both Table1Specific surface areas and average pore diameters for sand and various MOCSSurface area(m2g−1)Average pore diameter(˚A) Sand0.67451.42Unadsorbed a0.71242.77Adsorbed b0.55239.64Desorbed c0.70142.71a Without reacting with Pb(II)ions.b After reacting with Pb(II)ions.c After soaking with0.5mol l−1acid solution.390R.Han et al./Journal of Hazardous Materials B137(2006)384–395Fig.6.XPS detailed spectra of MOCS reacting with(a)copper;(b)lead. inner and surface porosity after adding the manganese oxides admixture.After reacting with Pb(II)ions,the pore size distribu-tion of MOCS had been changed,and parts of pores disappeared through the adsorption process.The results indicated the parts of pores were occupied with Pb(II)ions and average pore diameters decreased simultaneously,compared with unadsorbed MOCS, the surface area value of adsorbed MOCS is decreased,varying from of0.712to0.552m2g−1.Besides,pore size distribution of desorbed MOCS was similar to that of unadsorbed MOCS. The surface area of desorbed MOCS increased and average pore diameter also increased after regeneration with acid solution. The results indicated Pb(II)ions could be desorbed from the surface site of micropore and mesopores.3.5.Effect of contact time and temperature on Cu(II)andPb(II)adsorptionEffect of contact time and temperature on the adsorption of the copper(II)and lead(II)on MOCS was illustrated in Fig.7(a and b).The uptake equilibrium of Cu(II)and Pb(II) were achieved after180min and no remarkable changes were observed for higher reaction times(not shown in Fig.7).The shapes of the curves representing metal uptake versus time suggest that a two-step mechanism occurs.Thefirstportion Fig.7.Effect of contact time on Cu(II)and Pb(II)ions adsorption at pH4and various temperatures:(a)adsorption capacity vs.time;(b)adsorption percent vs.time(C0(Cu)=0.315mmol l−1,C0(Pb)=0.579mmol l−1).indicates that a rapid adsorption occurs during thefirst30min after which equilibrium is slowly achieved.Almost80%of total removal for both Cu(II)and Pb(II)occurred within60min.The equilibrium time required for maximum removal of Cu(II)and Pb(II)were90and120min at all the experimental temperatures, respectively.As a consequence,180min was chosen as the reac-tion time required to reaching pseudo-equilibrium in the present “equilibrium”adsorption experiments.Higher removal for cop-per and lead ions was also observed in the higher temperature range.This was due to the increasing tendency of adsorbate ions to adsorb from the interface to the solution with increasing temperature and it is suggested that the sorption of Cu(II)and Pb(II)by MOCS may involve not only physical but also chem-ical sorption.The metal uptake versus time curves at different temperatures are single,smooth and continuous leading to sat-uration,suggesting possible monolayer coverage of Cu(II)and Pb(II)on the surface of MOCS[40].3.6.Effect of pH on the sorption of Cu(II)and Pb(II)by MOCSIt is well known that the pH of the system is an important vari-able in the adsorption process.The charge of the adsorbate and the adsorbent often depends on the pH of the solution.The man-R.Han et al./Journal of Hazardous Materials B137(2006)384–395391 ganese oxide surface charge is also dependent on the solution pHdue to exchange of H+ions.The surface groups of manganeseoxide are amphoteric and can function as an acid or a base[41].The oxide surface can undergo protonation and deprotonationin response to changes in solution pH.As shown in Fig.8,the uptake of free ionic copper and leaddepends on pH,increasing with pH from1.4to5.1for Cu(II)and1.4to4.3for Pb(II).Above these pH levels,the adsorptioncurves increased very slightly or tended to level out.At low pH,Cu(II)and Pb(II)removal were inhibited possibly as result ofa competition between hydrogen and metal ions on the sorp-tion sites,with an apparent preponderance of hydrogen ions.Asthe pH increased,the negative charge density on MOCS sur-face increases due to deprotonation of the metal binding sitesand thus the adsorption of metal ions increased.The increase inadsorption with the decrease in H+ion concentration(high pH)indicates that ion exchange is one of major adsorption process.Above pH6.0,insoluble copper or lead hydroxide starts precip-itating from the solution,making true sorption studies impossi-ble.Therefore,at these pH values,both adsorption and precipita-tion are the effective mechanisms to remove the Cu(II)and Pb(II)in aqueous solution.At higher pH values,Cu(II)and Pb(II)inaqueous solution convert to different hydrolysis products.In order to understand the adsorption mechanism,the varia-tion of pH in a solution and the metal ions adsorbed on MOCSduring adsorption were measured,and the results are shown inFig.8.The pH of the solution at the end of experiments wasobserved to be decreased after adsorption by MOCS.Theseresults indicated that the mechanism by means of which Cu(II)and Pb(II)ion was adsorbed onto MOCS perhaps involved anexchange reaction of Cu2+or Pb2+with H+on the surface andsurface complex formation.According to the principle of ion-exchange,the more metalions that is adsorbed onto MOCS,the more hydrogen ions arereleased,thus the pH value was decreased.The complex reac-tions of Cu2+and Pb2+with manganese oxide may be writtenas follows(X=Cu,Pb and Y=Pb)[42]:MnOH+X2+ MnO−X2++H+(9)MnO−+X2+ MnO−X2+(10)Fig.8.Effect of pH on adsorption of Cu(II)and Pb(II)by MOCS.2(MnOH)+X2+ (MnO−)2X2++2H+(11)2(MnO−)+X2+ (MnO−)2X2+(12)MnOH+X2++H2O MnOXOH+2H+(13)MnOH+2Y2++H2O MnOY2OH2++2H+(14)Eqs.(9)–(14)showed the hydrogen ion concentration increasedwith an increasing amount of Cu(II)or Pb(II)ion adsorbed onthe MOCS surface.3.7.Effect of MOCS doseFig.9shows the adsorption of Cu(II)and Pb(II)as a functionof adsorbent dosage.It was observed that percent adsorptionof Cu(II)and Pb(II)increased from29to99%and19to99%with increasing adsorbent load from10to80g l−1,respectively.This was because of the availability of more and more bindingsites for complexation of Cu(II)ions.On the other hand,theplot of adsorption per unit of adsorbent versus adsorbent doserevealed that the unit adsorption capacity was high at low dosesand reduced at high dose.There are many factors,which can con-tribute to this adsorbent concentration effect.The most importantfactor is that adsorption sites remain unsaturated during theadsorption reaction.This is due to the fact that as the dosageof adsorbent is increased,there is less commensurate increasein adsorption resulting from the lower adsorptive capacity uti-lization of the adsorbent.It is readily understood that the numberof available adsorption sites increases by increasing the adsor-bent dose and it,therefore,results in the increase of the amountof adsorbed metal ions.The decrease in equilibrium uptake withincrease in the adsorbent dose is mainly because of unsaturationof adsorption sites through the adsorption process.The corre-sponding linear plots of the values of percentage removal(Γ)against dose(m s)were regressed to obtain expressions for thesevalues in terms of the m s parameters.This relationship is asfollows:for Cu(II):Γ=m s0.221+6.61×10−3m s(15)Fig.9.Effect of dosage of MOCS on Cu(II)and Pb(II)removal.。

托福阅读tpo60R-1原文+译文+题目+答案+背景知识

托福阅读tpo60R-1原文+译文+题目+答案+背景知识

TPO60 阅读-1 Underground Life原文 (1)译文 (2)题目 (3)答案 (7)背景知识 (7)原文Underground Life①Until about the late 1980s, most scientists believed that life was restricted to the top few meters of the soil or ocean sediments. The few reports of organisms being recovered from great depths within Earth were dismissed as contamination with material from the surface layers. Two technical developments changed this view. The first was the development of drilling techniques that gave confidence that samples could be retrieved from depth without contamination. Samples were recovered using a diamond-studded drill bit that headed a great length of rotating steel pipe from a drilling derrick. A concentrated tracer material was added to the lubricating fluid so that when a deep sample of rock was removed, any contaminated material could be identified and cut away to leave a pristine sample of rock from deep within Earth. The second development was the advent of techniques for identifying microorganisms without having to grow them in culture. All organisms contain DNA, and their presence can be revealed by dyes that either stain DNA directly or can be attached to nucleic acid probes. By varying the nucleic acid probe, scientists can demonstrate the presence of different types of microorganisms.②The first scientists to use these techniques were involved in the Subsurface Science Program of the United States Department of Energy (DOE). They were interested in the possibility that if organisms existed in the depths of Earth, they might degrade organic pollutants and help maintain the purity of groundwater or, rather less usefully, degrade the containers in which the DOE was proposing to deposit the radioactive waste from nuclear facilities. They demonstrated the presence of many different types of microorganisms in rocks at depths down to 500 meters beneath the surface. Since then, microbes have been discovered in many different types of rocks and deep within ocean sediments. The record depth at which life has been found is at the bottom of a South African gold mine, 3.5 kilometers below ground. Pressure and temperature increase as you go deeperinto Earth. Some scientists think that subsurface bacteria could withstand temperatures as high as 150℃. This would allow organisms to exist to depths of about 7 kilometers beneath the seafloor and to 4 kilometers below the surface of the land. Although the organisms are often sparsely distributed, this is such an enormous volume that it has been estimated that the total biomass of deep subsurface organisms exceeds that of those living on, or just below, the surface.③Bacteria are the most numerous of these subsurface organisms, but there are also fungi and protozoa. Some 10,000 strains of microorganism have been isolated from subsurface cores. Each gram of rock contains anything from 100 bacteria to 10 million bacteria(compared with more than 1 billion per gram in agricultural soils); ocean sediments contain even higher numbers. The protozoa feed on the bacteria, forming part of a simple subterranean food chain, but what do the bacteria feed on? Sedimentary rocks are formed from sands and from ocean, river, or lake sediments that have organic material trapped within them. Microbes living in pores within the sediments can utilize these ancient nutrients and grow. As sedimentary rocks are buried more deeply, they become increasingly compacted and their pores filled with minerals. The distribution of microorganisms is thus likely to become more patchy, condensed into the remaining pores and concentrations of nutrients. The bulk of Earth's crust, however, consists of igneous rocks, such as granite and basalt, which are solidified from molten magma. These rocks were too hot to support life when they were first formed; the organisms that inhabit cracks and fissures within the rocks are carried there by the groundwater flowing through them. Subsurface bacteria do not just rely on nutrients trapped within the rock or carried there by groundwater. Some are chemotrophs, deriving their energy from the oxidation of iron or sulfur compounds and building organic material directly from the carbon dioxide and hydrogen gas dissolved in the rock. These bacteria excrete organic compounds that are then utilized by other types of bacteria. These ecosystems based on chemotrophic bacteria are completely independent of material and solar energy from the surface.译文地下生活①直到大约20世纪80年代末,大多数科学家仍认为生命仅限于土壤或海洋沉积物的顶部几米。

药用昆虫桂花蝉共生放线菌的分离培养及抗菌活性研究

药用昆虫桂花蝉共生放线菌的分离培养及抗菌活性研究

广东药科大学学报Journal of Guangdong Pharmaceutical University Mar.2024,40(2)药用昆虫桂花蝉共生放线菌的分离培养及抗菌活性研究苏雅琳1,3,廖婧阳1,2,欧健鹏1,3,刘文彬1,2(1.广东药科大学基础医学院,广东广州510006;2.广东省生物活性药物研究重点实验室,广东广州510006;3.广东药科大学生命科学与生物制药学院,广东广州510006)摘要:目的探讨药用昆虫桂花蝉肠道共生放线菌的多样性,为抗菌药物开发提供新的微生物资源。

方法采用平板稀释法对桂花蝉共生放线菌进行分离和纯化;采用牛津杯法测定菌株抗菌活性;通过外观观察、扫描电镜和16SrDNA序列分析进行分类鉴定;对具有良好抗菌活性的菌株进行Nanopore第3代测序;利用Antismash、Prism、Circos、Rodigal、eggNOG、GO和KEGG等工具对基因组数据进行注释分析。

结果采用6种培养基从桂花蝉肠道共分离获得34株不同放线菌,其中链霉菌属(Streptomyces)32株、戈登氏菌属(Gordonia)1株和冢村氏菌属(Tsukamurella)1株,菌株GHC11可能为1株新的链霉菌种,73.5%的菌株对至少1种病原菌具有拮抗作用。

菌株GHC54具有显著的抗S.aureus和MRSA活性,通过形态学和分子生物学方法鉴定为Gordonia terrae。

菌株GHC54基因组大小为5346952bp,包含1个5210251bp环状染色体和1个136601bp质粒,共编码4828个基因,GC含量为67.91%,其中含有50个tRNA基因、9个rRNA基因。

编码基因分别进行eggNOG、GO、KEGG、Nr、Pfam、Swiss-prot和TrEMBL功能注释,共注释到4776个蛋白。

菌株GHC54中含有14个生物合成基因簇,包含6个NRPS、2个Terpene、1个Ectoine、1个Arylpolyene、1个Redox-cofactor、1个NAPAA、1个Ripp-like和1个PKS基因簇,85.7%的基因簇同源性小于20%,具有较高的新颖性。

彭巴效应作文范文

彭巴效应作文范文

彭巴效应作文范文英文回答:The Pengba effect, also known as the "Pengba phenomenon," refers to the situation where people tend to become more confident and motivated when they are praised or encouraged by others. This effect is named after a famous Chinese internet celebrity, Peng Peng, who gained popularity for his positive and optimistic attitude. When people receive positive feedback or compliments, they are more likely to believe in themselves and strive to achieve their goals.I remember a time when I was feeling really down about my work. I was struggling with a project and felt like I was making no progress. Then, a colleague of mine praised my efforts and told me that I was doing a great job. Suddenly, I felt a surge of motivation and confidence. I was able to push through the challenges and complete the project successfully. This experience made me realize thepower of the Pengba effect.The Pengba effect is not just about receiving praise, but also about giving it to others. When we encourage and support those around us, we can help them tap into their potential and achieve great things. I often try to use the Pengba effect in my interactions with friends and colleagues. I've noticed that when I praise and acknowledge their efforts, they become more determined and focused on their tasks.中文回答:彭巴效应,也被称为“彭巴现象”,指的是当人们受到他人的赞扬或鼓励时,他们往往会变得更加自信和积极。

重金属对木瓜蛋白酶的离子效应及作用机理

重金属对木瓜蛋白酶的离子效应及作用机理

AbstractPapain is a sulthydryl protease with high activity and stability. It has a wide applied future and high values of use in food, medicine, chemical industry for daily supplies and biological chemistry. At the same time, papain is one of the most widely studied enzymes of our time. The conditions of the papain hydrolysis on casein were optimized. On the basis of the general study on the activity of papain, the effects of Hg2+and Cu2+on papain were studied, and explored the action mechanism of the metal ions on papain. The enzyme hydrolysis process of glutin using papain was investigated. In the reaction system including Hg2+and Cu2+ions, the papain enzymatic hydrolysis was discussed under different conditions, which could be a theoretical and technological support for papain application in industry.The conditions such as temperature, pH, reaction time, substrate and enzyme concentrations could affect the activity of papain. Under the conditions of pH7 .0, substrate concentration 1.0mg/mL and enzyme concentration 2.0 mg/mL at 45ºC for 0.5h, the papain activity was the highest.There existed the dosage-response relationship between the metals and papain activity, which indicated the bimetal ions had Hormesis effect on the activity known as ―a low dose stimulation, high dose inhibition‖. When the concentration of Hg2+ was 10−6 mol/L and the concentration of Cu2+ was 10−8 mol/L , the relative papain activity reached the highest. When the concentration of Hg2+and the concentration of Cu2+ wre both 10-4 mol/L, the strongest effect of the bimetal ions on papain was obtained. Under low concentration, the papain was more sensitive to the stimulating effect of Cu2+ compared to Hg2+. However, Under high concentration, the inbibitional effect of Cu2+was not as good as Hg2+. Under low concentration, the bimetal ions exhibited synergistic activation effect on papain activity, and Cu2+ shielded Hg2+ inhibition on the activity at high concentration.The optimal reaction conditions of glutin hydrolysis were obtained, namely pH 7.0, glutin concentration 50.0 mg/mL, papain concentration 2.0 mg/mL at 45ºC for 1 h. In the case, the glutin hydrolysis degree was about 13%, and there existed a positive correlation between the effects of the bimetal ions on enzyme activity and on the glutin hydrolysis degree.When the concentrations of the bimetal ions Hg2+ and Cu2+ were 10-6 mol/L and 10-8mol/L, respectively, the strongest activity effect of the bimetal ions on papainwas obtained, and the content of the nonrand om secondary structures (α-helix and β-sheet) of the treated papain was the highest, the secondary structures of papain most stable, enzymatic affinity strongest and papain activity best. When the concentrations of Hg2+ and Cu2+ were both 10−4 mol/L, the ordered structure content and the papain activity were the lowest. The bimetal ions unfolded the enzymic protein and caused the destruction of the secondary structures. The results indicated that the order degree of papain conformation was correlated positively with the activity.The theoretical data from Tsou‘s theory on the kinetcs of irreversible modification of enzymic activity was well fitted to the experiment conclusions (R2>0.9926). This model could perfectly explain the Enzyme kinetics rule of the papain hydrolysis in the presence of the bimetal ions Hg2++Cu2+. The results showed that the effect of the bimetal ions Hg2++Cu2+was classified as mainly competitive type as an efficacious activator when the concentrations of the Hg2+ and Cu2+were 10-6 mol/L and 10-8 mol/L, respectively. On the other hand, the effect of Hg2++Cu2+ on papain was noncompetitive type as high inhibitor when the concentrations of the bimetal ions Hg2+ and Cu2+ were both 10-4 mol/L.Keyword: Bimetal ions Hg2++Cu2+; Papain ; Glutin; Secondary structure; Kinetics目录摘要 (i)Abstract (ii)第1章前言 (1)1.1 研究背景 (1)1.2 木瓜蛋白酶 (2)1.2.1 半胱氨酸蛋白酶简介 (2)1.2.2 木瓜蛋白酶简介 (3)1.3胶原、胶原蛋白、明胶与水解明胶 (4)1.3.1胶原、胶原蛋白、明胶与水解明胶简介 (4)1.3.2胶原、胶原蛋白、明胶以及水解明胶的结构区别 (6)1.4 水解明胶应用 (6)1.4.1 水解明胶在食品工业上的应用 (6)1.4.2 水解明胶在生物医药的应用 (7)1.4.3 水解明胶在化妆品行业的应用 (7)1.4.4水解明胶在其他行业的应用 (8)1.5 水解明胶的制备 (8)1.5.1 酸水解法 (8)1.5.2 碱水解法 (8)1.5.3 高温水解法 (9)1.5.4 酶水解法 (9)1.6 金属离子与酶 (9)1.6.1 金属离子与酶 (9)1.6.2 重金属离子、底物与酶 (10)1.7 国内外研究现状 (11)1.7.1 金属离子对酶作用的国内外研究现状 (11)1.7.2 木瓜蛋白酶酶解明胶国内外研究现状 (11)1.8 本课题研究内容和意义 (12)第2章木瓜蛋白酶酶解参数优化 (14)2.1 材料与仪器 (14)2.1.1 原料与试剂 (14)2.1.2 实验仪器 (14)2.2 实验方法 (15)2.2.1酪氨酸标准曲线 (15)2.2.2 木瓜蛋白酶酶活测定 (16)2.3 结果与讨论 (17)2.3.1 反应时间对酶活性的影响 (17)2.3.2 酶浓度对酶活性的影响 (18)2.3.3 pH值对酶活性的影响 (18)2.3.4 底物浓度对酶活性的影响 (19)2.3.5 温度对酶活性的影响 (20)2.4 结论 (21)第3章Hg2+、Cu2+对木瓜蛋白酶活性的影响 (22)3.1 材料与仪器 (22)3.1.1 实验仪器 (22)3.1.2 原料与试剂 (23)3.2 实验方法 (23)3.2.1 单金属离子对酶活影响 (23)3.2.2 双金属离子对酶活影响 (23)3.2.3 酶活测定方法 (23)3.3结果与讨论 (24)3.3.1 Hg2+或Cu2+对木瓜蛋白酶酶活的影响 (24)3.3.2 Hg2++Cu2+对木瓜蛋白酶活性的影响 (25)3.4结论 (27)第4章双金属离子对木瓜蛋白水酶解明胶的影响 (28)4.1 材料与仪器 (28)4.1.1 原料与试剂 (28)4.1.2 实验仪器 (29)4.2 实验方法 (29)4.2.1 蛋白含量测定 (29)4.2.2 木瓜蛋白酶水解明胶 (30)4.3 结果与讨论 (31)4.3.1 水解时间对明胶水解度的影响 (31)4.3.2 pH值对明胶水解度的影响 (32)4.3.3 水解温度对明胶水解度的影响 (33)4.3.4 底物浓度对明胶水解度的影响 (34)4.3.5 酶浓度对明胶水解度的影响 (34)4.3.6 双金属离子Hg2++Cu2+对酶水解明胶的影响 (35)4.4 结论 (36)第5章Hg2++Cu2+双金属对木瓜蛋白酶作用机理 (37)5.1 材料与仪器 (37)5.1.1 原料与试剂 (37)5.1.2 实验仪器 (37)5.2 实验方法 (38)5.2.1 傅里叶红外 (38)5.2.2 紫外吸收光谱 (38)5.2.3 荧光发射光谱 (38)5.3结果与讨论 (38)5.3.1 FT-IR分析 (38)5.3.2木瓜蛋白酶荧光发射光谱 (42)5.3.3木瓜蛋白酶紫外吸收光谱结构 (43)5.4 结论 (45)第6章双金属Hg2++Cu2+作用下酶解动力学 (46)6.1 材料与仪器 (46)6.1.1 原料与试剂 (46)6.1.2 实验仪器 (47)6.2实验方法 (47)6.2.1木瓜蛋白酶酶活测定 (47)6.2.2溶液配置 (47)6.3 测定方法 (47)6.3.1木瓜蛋白酶活性不可逆动力学 (47)6.4 结果与讨论 (49)6.4.1 米氏常数K m (49)6.4.2 双金属Hg2++Cu2+存在下木瓜蛋白酶动力学特征 (50)6.5 结论 (55)第7章结论与展望 (56)7.1 结论 (56)7.2 创新点 (57)7.3 展望 (57)参考文献 (58)致谢 (63)附录 (64)第1章前言1.1 研究背景木瓜蛋白酶[EC3.4.22.2] (papain)属于半胱氨酸蛋白酶的一种,半胱氨酸蛋白酶(EC 3.4.22)又称巯基蛋白酶,参与很多动植物生理过程,有着极其广泛的用途,但它也是Hg2+、Cu2+等重金属离子及其化合物作用的潜在靶点[1],使其工业应用受到限制,因此,深入探究重金属离子与酶的作用机理,为拓宽木瓜蛋白酶的应用范围,提高酶活性奠定理论基础。

膳食纤维对肠道菌群影响的研究进展

膳食纤维对肠道菌群影响的研究进展

第2期(总第521期)2021年2月农产品加工Farm Products ProcessingNo.2Feb.文章编号:1671-9646(2021) 02a-0067-06膳食纤维对肠道菌群影响的研究进展谢 静,马梦婷,陈小静,许泽坤,李紫君,**隋中泉收稿日期:2020-07-20基金项目:国家自然科学基金项目(31671893)。

作者简介:谢静(1987—),女,硕士,研究方向为碳水化合物。

*通讯作者:隋中泉(1981—),女,博士,教授,研究方向为碳水化合物。

(上海交通大学农业与生物学院食品科学系,上海200240)摘要:膳食纤维不能被人体小肠消化吸收,可在大肠中完全或部分发酵,是肠道微生物的主要能量来源。

膳食纤维 具有不同的结构特征,其降解受一系列碳水化合物活性酶(CAZymes )的控制。

肠道微生物则是通过编码的碳水化合物活性酶利用膳食纤维,而其表达该酶的基因数量和基因类型具有差异,膳食纤维的选择性消耗决定了肠道中哪个细菌类群受到青睐并可以影响结肠中菌种和菌株的平衡。

因此,膳食纤维的类型会影响菌群的种类和数量。

介绍了 膳食纤维和碳水化合物活性酶的定义和分类,并总结了特定的膳食纤维类型(抗性淀粉、果胶、纤维素、半纤维素和菊粉)对肠道微生物组成的影响,旨在为膳食纤维对肠道菌群和健康的研究提供理论参考。

关键词:膳食纤维;肠道微生物;碳水化合物活性;研究进展中图分类号:TS272 文献标志码:A doi : 10.16693/ki.1671-9646(X ).2021.02.015Research Progress in the Effect of Dietary Fiber Structures onthe Gut MicrobiotaXIE Jing, MA Mengting, CHEN Xiaojing, XU Zekun, LlZijun, *S UI Zhongquan(Department of Food Science , School of Agriculture and Biology , Shanghai Jiao Tong University , Shanghai 200240, C h ina )Abstract : Dietary fibers are resistant to digestion and absorption in the human small intestine with complete or partial fermen ­tation in the large intestine , which are the main source of energy for the bacteria of the colon. Dietary fibers bear differentstructural features and the breakdown of dietary fibers is controlled by a series of carbohydrate-active enzymes (CAZymes ). Dietary fiber utilization ability of gut microbes depends on gene content of C A Zymes that encodes. The difference in the number and type of genes expressing C A Zymes that microorganisms possess suggests that selective consumption of dietary fibers deter ­mines which bacterial groups are favored in the gut and influence the balance of species and strains in the colon. Therefore ,the types of dietary fiber influence the kinds and numbers of bacterial groups. The review systematically introduced the defini ­tion and classification of dietary fiber and AZymes , and summarizesd the impact of specific dietary fiber types ( resistant starch , pectin , cellulose , hemicellulose and inulin ) on the composition of gut microbiota , in order to provide a theoretical reference for the study of dietary fiber on gut microbiota and health.Key words : dietary fibers ; gut microbiota ; carbohydrate-active enzymes ; research progress膳食纤维是不能被人体消化的多糖类物质和木 质素的总称,也被称为第七营养素,根据其溶解性 不同可分为水不溶性膳食纤维和水溶性膳食纤维两 大类。

加剧失衡现象英文作文

加剧失衡现象英文作文

加剧失衡现象英文作文英文:The exacerbation of the imbalance phenomenon is a global issue that has been affecting many countries. This phenomenon refers to the widening gap between the rich and the poor, the unequal distribution of resources, and the growing disparities in social status and opportunities. The root cause of this problem is complex and multifaceted, but it is mainly attributed to the unequal distribution of wealth, power, and opportunities in society.One of the main reasons for the exacerbation of the imbalance phenomenon is the uneven distribution of resources. In many developing countries, resources such as land, water, and minerals are controlled by a small group of elites, leaving the majority of the population withlittle or no access to these resources. This results in a situation where the rich get richer, while the poor get poorer.Another factor that contributes to the imbalance phenomenon is the lack of access to education and healthcare. In many countries, the poor have limited access to quality education and healthcare, which limits their opportunities for social mobility and economic advancement. This creates a vicious cycle of poverty and inequality that is difficult to break.Furthermore, the concentration of wealth and power in the hands of a few individuals or corporations is also a significant contributor to the imbalance phenomenon. This concentration of power often leads to the exploitation of workers, the degradation of the environment, and the erosion of democratic institutions.In conclusion, the exacerbation of the imbalance phenomenon is a complex issue that requires a multifaceted approach to address. Governments, civil society organizations, and individuals all have a role to play in promoting equality, social justice, and sustainable development.中文:加剧失衡现象是一个全球性问题,影响着许多国家。

Urbanizations Effect on Rural Communities

Urbanizations Effect on Rural Communities

Urbanizations Effect on RuralCommunitiesUrbanization has been a significant trend in many countries around the world, with more and more people moving from rural areas to urban centers in search of better opportunities and a higher standard of living. While urbanization has brought about numerous benefits for those living in cities, it has also had a profound impact on rural communities. This impact is multifaceted, affecting various aspects of rural life such as economy, culture, and environment. One of the most significant effects of urbanization on rural communities is the depletion of the rural labor force. As people migrate to cities in search of better job prospects, rural areas are left with a dwindling population, particularly of working-age individuals. This exodus of people has a detrimental effect on thelocal economy, as there are fewer people available to work in agriculture, whichis often the primary industry in rural areas. This can lead to a decline in the productivity and competitiveness of rural economies, further exacerbating thecycle of migration to urban areas. Furthermore, the outflow of people from rural communities to urban centers can result in a loss of traditional skills and knowledge that are essential to rural livelihoods. As younger generations leave their rural homes, they often abandon traditional practices and ways of life in favor of the more modern and fast-paced urban lifestyle. This can lead to a lossof cultural identity and heritage in rural communities, as well as a decline inthe preservation of local traditions and crafts. Additionally, urbanization can have a significant impact on the environment in rural areas. As more people moveto urban centers, there is an increased demand for resources such as water, energy, and food, which often leads to the exploitation and degradation of rural natural resources. This can have devastating effects on the local environment, leading to deforestation, soil erosion, and pollution. Furthermore, the expansion of urban areas often encroaches on rural land, leading to the destruction of naturalhabitats and wildlife. On the other hand, it is important to acknowledge that urbanization can also bring about positive changes for rural communities. For example, the migration of people to cities can lead to an increase in remittancessent back to rural areas, which can help to alleviate poverty and improve living standards for those who remain in rural communities. Additionally, urbanization can lead to the development of infrastructure and services in rural areas, such as improved road networks, healthcare facilities, and educational institutions, which can benefit the local population. In conclusion, the effects of urbanization on rural communities are complex and multifaceted, impacting various aspects of rural life. While urbanization can lead to the depletion of the rural labor force, a loss of traditional skills and knowledge, and environmental degradation, it can also bring about positive changes such as increased remittances and the development of infrastructure and services. It is essential for policymakers to consider these diverse impacts and to develop strategies that can help to mitigate the negative effects of urbanization on rural communities, while also harnessing the potential benefits that it can bring.。

腐植酸型营养剂对潞党参产量与品质的影响

腐植酸型营养剂对潞党参产量与品质的影响

山西农业科学 2023,51(7):771-776Journal of Shanxi Agricultural Sciences腐植酸型营养剂对潞党参产量与品质的影响程泽京1,张慧仙2,黄高鉴1,郭军玲1,张强1,杨治平1(1.山西农业大学土壤环境与养分资源山西省重点实验室,山西太原 030031;2.陵川县职业中学,山西陵川 048300)摘要:采用大田试验,以农户习惯(喷施植物生长调节剂矮壮素)为对照,同时设置清水(T0)、腐植酸制剂Ⅰ(T1)、腐植酸制剂Ⅱ(T2)和腐植酸制剂Ⅰ+促根营养制剂(T3)处理,探究腐植酸型营养剂对潞党参生长性状和品质的影响,并通过隶属函数法进行综合评价,确定最适宜潞党参的腐植酸型营养剂。

结果表明,喷施不同类型腐植酸型营养剂后,T3处理的根长最大,较T0、T1处理分别显著增加7.73%和6.83%;T0处理的钾素累积量显著低于其余各处理,分别较CK、T1、T2和T3处理降低了18.13%、9.18%、13.03%和16.48%;T1、T2、T3处理产量均显著高于T0处理,且T3处理产量与CK间差异不显著,较T0显著增加19.74%;潞党参的水分、总灰分和浸出物含量均达到了中国药典(2020版)规定;T3处理的多糖和炔苷含量最高,分别较CK、T0处理显著提高49.97%、25.25%和78.95%、30.77%。

通过隶属函数法综合评价,腐植酸制剂Ⅰ+促根营养制剂处理效果最佳,能在提高潞党参产量的同时改善品质,实现高产优质。

关键词:潞党参;腐植酸;隶属函数法;产量;品质中图分类号:R282.71 文献标识码:A 文章编号:1002‒2481(2023)07‒0771‒06Effects of Humic Acid Conditioners on the Yield and Quality ofCodonopsis pilosula(Lu Dangshen)CHENG Zejing1,ZHANG Huixian2,HUANG Gaojian1,GUO Junling1,ZHANG Qiang1,YANG Zhiping1(1.Shanxi Provincial Key Laboratory of Soil Environment and Nutrient Resources,Shanxi Agricultural University,Taiyuan 030031,China;2. Lingchuan County Vocational High School,Lingchuan 048300,China)Abstract:In this study, five treatments were conducted to determine effect of humic acid conditioners on the growth traits and quality of Codonopsis pilosula, the treatments were plant growth conditioner farmers are used to applying(CK), pure water (T0), humic acid conditioner I(T1), humic acid conditioner II(T2) and humic acid conditioner I + root-promoting growth conditioner(T3), and comprehensive evaluation was conducted through the membership function method to determine the humic acid conditioner the most most suitable for Codonopsis pilosula. The results showed that after spraying different types of humic acid conditioners, the root length of T3 treatment was the largest, which was significantly increased by 7.73% and 6.83% compared with T0 and T1 treatments. The potassium accumulation of T0 treatment was significantly lower than that of the other treatments, which was 18.13%, 9.18%, 13.03%, and 16.48% lower than that of CK, T1, T2, and T3, respectively. The yield of T1, T2,and T3 treatments was significantly higher yields than that of the T0 treatment, and there was no significant difference in the yield between T3 and CK, the yield under T3 was increased by 19.74% compared with T0. The content of moisture, total ash and extract of Codonopsis pilosula reached the standard of the Chinese Pharmacopoeia(2020 edition). The content of polysaccharide and lobetyolin under T3 was significantly increased by 49.97% and 78.95% compared with CK, respectively, and the value was significantly increased by 25.25% and 30.77% compared with T0, respectively. Humic acid conditioner I + root-promoting growth conditioner had the best effects on increasing the yield and simultaneously improving quality of Codonopsis pilosula by the comprehensive evaluation based on membership function method.Key words:Codonopsis pilosula; humic acid; membership function method; yield; quality潞党参为《中国药典》2020版中所列的桔梗科多年生草本植物党参(Codonopsis piloula (Franch.)Nannf.)的干燥根[1],其含有聚炔类、皂苷类和多糖类等多种成分[2],具有健脾益肺、益气养血等功效[3],doidoi:10.3969/j.issn.1002-2481.2023.07.08收稿日期:2022-11-20基金项目:国家重点研发计划项目(2019YFC1710800)作者简介:程泽京(1999-),男,山西临汾人,在读硕士,研究方向:植物营养。

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a r X i v :c o n d -m a t /0212385v 1 [c o n d -m a t .s u p r -c o n ] 16 D e c 2002Effects of Boron Purity,Mg Stoichiometry and Carbon Substitution on Properties of Polycrystalline MgB 2R.A.Ribeiro,S.L.Bud’ko,C.Petrovic,P.C.Canfield Ames Laboratory and Department of Physics and Astronomy Iowa State University,Ames,IA 50011USA 1Introduction Since the discovery of superconductivity in the compound MgB 2by Akim-itsu and co-workers [1,2],considerable progress has been made in the un-derstanding of the fundamental properties of this material.Within weeks of the announcement of this discovery,it was established that high purity,very low residual resistivity samples of MgB 2could be synthesized by ex-posing boron powder or filaments to Mg vapor at temperatures at or near 950◦C for as little as two hours [3,4,5].Samples with residual resistivity ratio[RRR =R (300K )/R (42K )]values in excess of 20and residual resistivities aslow as0.4µΩcm were synthesized by this method.Such a low resistivity in an intermetallic compound with a superconducting critical temperature,T c, near40K was of profound physical,as well as engineering,interest.The im-plications of this high RRR and lowρ0ranged from large magneto-resistances to questions of how a material with such an apparently large electron-phonon coupling could have such a small normal state resistivity.On the applied side, a normal state resistivity of0.4µΩcm for temperatures just above T c means that MgB2wires would be able to handle a quench with much greater ease than,for example,Nb3Sn wires which have aρ0that is over an order of mag-nitude larger for T∼20K[5].Unfortunately,other techniques of synthesizing MgB2had difficulties in achieving such high RRR or lowρ0values[6,7,8,9,10]. In some cases,the authors of these papers have concluded that the resistivity of their samples must be the intrinsic resistivity and that higher RRR values or lower residual resistivity values must somehow be extrinsic.In order to ad-dress these concerns and in order to shed some light on how low resistivity samples can be grown,we have studied the effects of boron purity and magne-sium stoichiometry on sintered pellet samples.Based on these measurements, we conclude that the purity of the boron used to make the MgB2is a dominant factor in determining the ultimate,low temperature,normal state resistivity of the sample,and that RRR values as high as20and residual resistivities as low as0.4µΩcm are intrinsic materials properties of high purity MgB2[11]. Once reproducible synthesis of high purity,single phase,MgB2is understood and believed to be somewhat controllable,the next question to be addressed is:can MgB2be doped in a reliable manner?Whereas the effects of Al sub-stitution for Mg were addressed very early on[12,13,14],substitutions on the boron site have been somewhat more difficult.There have been some attempts to substitute carbon for boron[15,16,17,18]with results varying from very lit-tle effect on T c[15]to shift of T c down to∼35K[16,17]or32K[18]depending upon the nominal carbon concentration as well as the sample synthesis route. By far the most appealing route to producing carbon doped MgB2is to start with the carbon mixed with the boron on the length scale of a unit cell.Start-ing with a boron rich compound such as B4C appears to offer just such a route[18].In order to determine how to synthesize as close to a single phase sample as possible we have measured powder X-ray diffraction spectra as well as temperature dependent magnetic susceptibility and electrical transport on a series of samples synthesized at different temperatures.2Sample synthesisSamples of MgB2for this study were made in the form of sintered pellets.The sintered pellets were made by sealing stoichiometric amounts of Mg(99.9%) and B into Ta tubes,placing these tubes(sealed in quartz)into furnacesheated to950◦C for3hours,and then quenched to room temperature[3]. For the initial studies of the effects of boron purity,stoichiometric MgB2was synthesized and the quality of the boron was varied.For the studies of mag-nesium stoichiometry,nominal stoichiometries that ranged from Mg0.811B2to Mg1.211B2were used and samples were synthesized with99.95%pure,isotopi-cally enriched11B[11].Given that our synthesis technique involves a reaction between solid boron and Mg vapor we felt that any attempt at boron site substitution required that the dopant and the boron be mixed at an atomic level before exposure to Mg vapor.The compound B4C is ideal given that it is boron rich and includes carbon-a likely dopant.Earlier work[18]indicated this may be a viable route,but also appeared to be somewhat preliminary.The carbon doped MgB2 sintered pellets were made by sealing lumps of Mg(99.9%)and B4C(99%-Alfa Aesar)into Ta tubes,following same procedure for the pure MgB2,and heating to a variety of temperatures.For this work,the samples were heated for24hours to four different temperatures:(750◦C,950◦C,1100◦C,1200◦C). In order to compare our samples with the initial studies using B4C as starting reagent(Mickelson et al.[18]),we also prepared samples by heating to600◦C for2hours and then700◦C for2more hours.The initial stoichiometric ratio in all these procedures was5:2of Mg:B4C giving a nominal composition of Mg(B0.8C0.2)2.A.C.electrical resistance measurements were made using Quantum Design MPMS and PPMS units.Platinum wires for standard four-probe configuration were connected to the samples with Epotek H20E silver epoxy.LR400and LR700A.C.resistance bridges were used to measure the resistance when the MPMS units were used to provide the temperature environment.Powder X-ray diffraction measurements were made using a Cu Kαradiation in a Scintag diffractometer and a Si standard was used for all runs.The Si lines have been removed from the X-ray diffraction data,leading to apparent gaps in the powder X-ray spectra.3Effects of Boron PurityFigure1presents powder X-ray diffraction spectra for three samples with varying nominal boron purities:90%purity,99.99%purity,and the99.95% purity,isotopically pure11B.By comparing the two upper panels to the bottom panel it can be seen that the strongest MgB2lines are present in all three samples.The spectrum shown in the upper panel,the data taken on the sample made from boron with only a90%nominal purity,also has weak Mg and MgO lines present.This is not inconsistent with the fact that the primary impurity in the90%boron is associated with Mg.Figure2displays the normalized resistance,R(T)/R(300K),of MgB2pellets that were made using thefive different types of boron powderas described in Table1.Each curve is the average of three resistance curves taken on different pieces broken offof each pellet.Figure2demonstrates that RRR values can range from as low as4to as high as20depending upon what source of boron is used.Among the natural boron samples examined there is a steady increase in RRR as the purity of the source boron is improved.The MgB2synthesized from the isotopically pure boron appears to have the best RRR,although it’s nominal purity is somewhat less than that of the99.99%pure natural boron, but those skilled in the art will realize that claims of purity from different companies can vary dramatically.In addition,it is likely that the isotopically pure boron was prepared in a somewhat different manner from the other boron powders used(very likely using a boronfluoride or boric acid or any of its complexes as an intermediate phase,in order to achieve isotopic separation). The primary point thatfigure2establishes is that the purity of the boron used can make a profound difference on the normal state transport properties. In Fig.3the same resistance data is plotted,but instead of simply normalizing the data at room temperature the data is normalized to the temperature derivative at room temperature.This is done to see if the resistance curves differ only by a temperature independent residual resistivity term:i.e.this normalization is based upon the assumption that the slope of the temperature dependent resistivity at room temperature should be dominated by phonon scattering,and therefore be the same for each of these samples.As can be seen,this seems to be the case,at least to thefirst order.By using higher purity boron we are able to diminish the additive,residual resistance by a factor of approximatelyfive.The insets tofigs.2and3indicate that there is a monotonic improvement in T c as the boron purity(or RRR value)is increased.T c values vary from just below38K to just above39K depending upon which boron is used.It should be noted that similar behavior have been seen in other polycrystalline samples with poor RRR values[6,7,8,9,10].Based upon these results,we choose the isotopically pure11B for the further study of the effects of Mg stoichiometry on MgB2pellet samples.But before we proceed to the next section,it is worth noting that one of the difficulties associated with the samples made by other research groups may well be due to the use of boron with less than the highest purity.In addition,to our knowledge very few other groups have been using the Eagle-Picher isotopically pure boron in the samples for electrical transport measurements.It should be noted though that recent measurements[19]have reproduced these results using Eagle-Picher11B.4Effects of Magnesium StoichiometryIn order to study the effect of magnesium stoichiometry on the transport prop-erties of Mg11B2,a series of Mg x11B2(0.8≤x≤1.2)samples were synthesized. Figure4presents powder X-ray diffraction patterns for the extreme members of the series(top and bottom panels)as well as for the stoichiometric Mg11B2 (middle panel).In all cases the lines associated with the Mg11B2phase are present.For the Mg0.811B2sample,there is a weak line seen at2θ=35.8◦that is associated with MgB4(marked with a+).This is consistent with the fact that there was insufficient Mg present to form single phase Mg11B2.For the Mg1.211B2sample there are strong diffraction lines associated with Mg (marked with*).This too is consistent with the stoichiometry of the sample: Mg11B2is the most Mg-rich member of the binary phase diagram,therefore any excess Mg will end up as unreacted Mg.The X-ray diffraction pattern for the stoichiometric Mg11B2shows much smaller peaks associated with a small amount of both MgB4and Mg phases.This pattern is different from the one shown in Fig.2in that this sample was reacted for3hours,whereas the sample used in Fig.1was reacted for4hours.Given that all of the samples used for the Mg-stoichiometry study were reacted for3hours,it is appropri-ate to show this powder diffraction set along with the other members of the series.It should be noted that there is continuous change in the nature of the second phases in the samples.For Mg deficient samples there is only MgB4 as a second phase.For the stoichiometric Mg11B2samples there are either no second phases or very small amounts of both MgB4and Mg(depending upon reaction times),and for the excess Mg samples there is no MgB4,but clear evidence of excess Mg.Figure5presents normalized resistance data forfive representative Mg x11B2 pellets.In each case the curve plotted is the average of three or more samples cut from the same pellet.There is far less variation between the different pellets in this case than there was for the case of boron purity(Fig.2).This is most clearly illustrated by the fact that the values of the R(T)collapse almost completely onto a single manifold as viewed on full scale.Figure6 plots the RRR values for each of the individual samples(shown as the smaller symbols)as well as the RRR of the average curve.As can be seen,the RRR values increase slowly from∼14for Mg0.811B2to∼18for Mg11B2.This is followed by an increase in RRR values for excess Mg,with Mg1.211B2having an RRR value of∼24.The important point to note is that even,for the most Mg deficient sample,the lowest measured RRR value is significantly greater than10.At no point in this series wefind samples with RRR values of3,6, or10,even when a clear MgB4second phase is present.For samples ranging from Mg0.911B2to Mg1.111B2(dotted box infigure6)the average RRR values cluster around RRR=18±3.These data indicate that,for sintered pellets, RRR values of18can be associated with stoichiometric Mg11B2in pellet form.Whereas the effects of excess Mg are relatively minor in these samples(given their low intrinsic resistivities),these effects can still be clearly seen.In ad-dition to the increase in the RRR value,there is a change in the form of the temperature dependence of the resistance.This can be best seen in Fig.7, in which the resistance data have been normalized to its room temperature slope.The data for all x values less than1.0are similar(to within small dif-ferences in residual resistivity)and can be collapsed onto a single curve.On the other hand,the resistance data for the x=1.1and x=1.2are qualita-tively different.They start out with somewhat higher normalized resistance data than the stoichiometric sample,and then below100K cross below the stoichiometric sample.This is shown in Fig.7by representing the data for x=1.2as a dashed line and can also be seen in the inset(stars).This change in behavior is very likely due to the increasing effects of having Mg in parallel (and series)with the MgB2grains.As can be seen in Fig.7,this effect becomes larger as the amount of excess Mg is increased.This deviation from the MgB2 resistance curve may actually serve as a diagnostic for the detection of excess Mg.For further details about the effects of boron purity,Mg stoichiometry or the results of our studies on MgB2wires segments see reference[11].5Carbon dopingFigure8presents the powder X-ray diffraction patterns for nominal Mg(B0.8C0.2)2 samples reacted for24hours at temperature of750,950,1100and1200◦C. The top pattern is from a sample that was reacted for2hours at600◦C and then reacted for2more hours at700◦C.This sample was made using the temperature/time schedule outlined in reference[18]and serves as a point of comparison.There is a clear decrease in the signal coming from impurity phases in the material as the reaction temperature is increased.The reactions carried out at either1100or1200◦C appear to be approaching single phase. The temperature dependent magnetic susceptibility and electrical resistance for these samples are presented in Figs.9and10respectively.As the phase pu-rity of the material is improving the onset temperature(see insets)decreases and the transition sharpens.The sample synthesized at1200◦C for24hours has T c=22.7K based on zero resistance criterion and T c=21.9K based on an onset of diamagnetism criterion.It should be noted that,based on the magnetization data,for the sample synthesized at950◦C the majority of the sample appears to have a T c∼16K,well below the onset temperature of 23.5K.This,as well as the other transition temperatures found for samples reacted at750◦C or lower temperature may well be associated with inhomo-geneities in these samples and may indicate that even further carbon dopinglevels are possible.In addition,there is still a slight increase in T c when the reaction temperature is increased from1100◦C to1200◦C.This may indicate that a further increase in reaction time or temperature will yield some further (slight)increase in T c.These data represent afirst step in the optimization and study of carbon doped MgB2with the nominal composition of Mg(B0.8C0.2)2.A more detailed study is part of an ongoing research project.6ConclusionIn summary,through the synthesis of various MgB2samples with different nominal boron purities we found values of RRR from4to20,which covers almost all values found in literature.To obtain high values of RRR,high purity reagents are necessary.With the isotopically pure boron we obtained the highest RRR∼20for the stoichiometric compound.We also investigated Mg x11B2samples with0.8<x<1.2.These have shown that from the most Mg deficient samples we observe inclusions of the MgB4phase,and no evidence of Mg.For samples with excess Mg we do not observe any MgB4.For the range Mg0.811B2up to Mg1.211B2we found average values of RRR between14 and24.For smaller variations in stoichiometry(x=1±0.1)RRR=18±3. All of our data point to the conclusion that high RRR(≥20)and lowρ0 (≤0.4µΩcm)are intrinsic materials properties associated with high purity MgB2[11].Our initial work on optimizing the formation of carbon doped MgB2via the use of B4C indicates that nearly single phase material can be formed by reaction of nominal Mg(B0.8C0.2)2for24hours at1200◦C.The T c for this composition is between21.9K and22.7K(depending on criterion for T c used).Further work on the optimization and characterization of this compound is ongoing,but it appears that Mg(B0.8C0.2)2may offer a very useful window on the rather novel physics associated with MgB2.AcknowledgementsAmes Laboratory is operated for the US Department of Energy by Iowa State University under Contract No.W-7405-Eng-82.This work was supported by the Director for Energy Research,Office of Basic Energy Sciences.The authors would like to thank N.Kelson for drawing our attention to earlier research on the properties of MgB2[20],M.A.Avila,D.K.Finnemore and N.E.Anderson, Jr.for helpful assistance and many fruitful discussions.References[1]J.Akimitsu,Symposium on Transition Metal Oxides,Sendai,January10,2001.[2]J.Nagamatsu,N.Nakagawa,T.Muranaka,Y.Zenitani and J.Akimitsu,Nature410(2001)63.[3]S.L.Bud’ko,pertot,C.Petrovic,C.E.Cunningham,N.Anderson andP.C.Canfield,Phys.Rev.Lett.86(2001)1877.[4] D.K.Finnemore,J.E.Ostenson,S.L.Bud’ko,pertot and P.C.Canfield,Phys.Rev.Lett.86(2001)2420.[5]P.C.Canfield,D.K.Finnemore,S.L.Bud’ko,J.E.Ostenson,pertot,C.E.Cunningham and C.Petrovic,Phys.Rev.Lett.86(2001)2423.[6]X.H.Chen,Y.S.Wang,Y.Y.Xue,R.L.Meng,Y.Q.Wang and C.W.Chu,Phys.Rev.B65(2002)024502.[7]Sang Young Lee,J.L.Lee,Jung Hun Lee,J.S.Ryu,J.Lim,S.H.Moon,H.N.Lee,H.G.Kim and B.Oh,Appl.Phys.Lett.79(2001)3299.[8] A.K.Pradhan,Z.X.Shi,M.Tokunaga,T.Tamegai,Y.Takano,K.Togano,H.Kito and H.Ihara,Phys.Rev.B64(2001)212509.[9]Kijoon H.P.Kim,Jae-Hyuk Choi,C.U.Jung,P.Chowdhury,Hyun-Sook Lee,Min-Seok Park,Heon-Jung Kim,J.Y.Kim,Zhonglian Du,Eun-Mi Choi,Mun-Seog Kim,W.N.Kang,Sung-Ik Lee,Gun Yong Sung,Jeong Yong Lee,Phys.Rev.B65(2002)100510.[10]Y.Y.Xue,R.L.Meng,B.Lorenz,J.K.Meen Y.Y.Sun and C.W.Chu,Physica C377(2002)7.[11]R.A.Ribeiro,C.Petrovic,S.L.Bud’ko and P.C.Canfield,Physica C382(2002)194.[12]J.S.Slusky,N.Rogado,K.A.Regan,M.A.Hayward,P.Khalifah,T.He,K.Inumarul,S.Loureiro,M.K.Hass,H.W.Zandbergen and R.J.Cava,Nature 410(2001)343.[13]B.Lorenz,R.L.Meng,Y.Y.Xue and W.Chu,Phys.Rev.B64(2001)052513.[14]O.de la Pe˜n a,A.Aguayo and R.de Coss,Phys.Rev.B66(2002)012511.[15]M.Paranthaman,J.R.Thompson and D.K.Chirsten,Physica C355(2001)1.[16]J.S.Ahn and E.J.Choi,cond-mat/0103169.[17]T.Takenobu,T.Ito,D.H.Chi,K.Prassides and Y.Iwasa,Phys.Rev.B64(2001)134513.[18]W.Mickelson,J.Cumings,W.Q.Han and A.Zettl,Phys.Rev.B65(2002)052505.[19]V.Braccini,L.D.Cooley,S.Patnaik,P.Manfrinetti,A.Palenzona,A.S.Siriand rbalestier,cond-mat/0208054.[20]L.I.Kostantinova,B.A.Katsnelson,L.K.Konysheva,N.N.Loboda,CurrentToxicology1(1993)23.TableTable1:Boron form and purity(as provided by the seller).Figure1:Powder X-ray(Cu Kαradiation)diffraction spectra of stoichiomet-ric MgB2(with h,k,l)for3different boron qualities(a)90%pure natural boron;(b)99.99%pure natural boron and(c)99.95%pure isotopic enriched 11B.Samples(a)and(b)were synthesized for3h/950◦C,and sample(c)for 4h/950◦C.The data gaps are due to the removal of the Si peaks.Figure2:Variation of the normalized zero-field resistance as a function of temperature for MgB2pellets with different boron purities.Inset:expanded scale near T c.Figure3:Resistance curves normalized by their temperature derivative at room temperature,for different boron purities.Inset:expanded scale near T c.Figure4:X-ray spectra for3different nominal compositions of Mg x11B2for x=0.8,1.0,1.2.Figure5:Temperature dependence of the normalized resistance for represen-tative samples with nominal composition Mg x11B2(0.8<x<1.2).Inset: expanded scale near T c.Figure6:Residual resistance ratio of Mg x11B2(0.8<x<1.2).The open symbols represent different pieces selected from the same batch.The solid symbols are the average.The dotted box delimits the smaller variation(x= 1±0.1).Figure7:Resistance curves normalized by temperature derivative at room temperature,for Mg x11B2(x=0.8,0.9,1.0,1.1and1.2).x=1.2data shown as dashed curve as discussed in the text.Inset:expanded scale near T c. Figure8:Powder X-ray diffraction spectra of Mg(B0.8C0.2)2(with h,k,l)for samples that were synthesized for(a)2hours at600◦C and then2hours at 700◦C;(b)24hours at750◦C;(c)24hours at950◦C;(d)24hours at1100◦C and(d)24hours at1200◦C.The data gaps are due to the removal of the Si peaks.Symbols:+=B4C,∗=MgB2C2and#=Mg2C3,as indicated in figure.Figure9:Temperature dependent magnetic susceptibility for representative Mg(B0.8C0.2)2samples taken in H=50Oe appliedfield:ZFC-warming. Inset:expanded temperature range near T c.Figure10:Normalized resistance as a function of temperature for Mg(B0.8C0.2)2 samples synthesized at different reaction temperatures.Inset:expanded tem-perature range near T c.Purity Source 90%Alfa Aesar 95%Alfa Aesar 98%Alfa Aesar 99.95%Eagle-Picher 99.99%Alfa AesarFigure1Figure2Figure3Figure4Figure5Figure6Figure7Figure8Figure9Figure10。

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