A three-site Langmuir adsorption model to elucidate the temperature, pressure, and support

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纳米纤维素晶体和纤丝制备及其气凝胶吸附特性研究

纳米纤维素晶体和纤丝制备及其气凝胶吸附特性研究

摘要随着环境的日益恶化以及化石能源的匮乏,为了减缓二氧化碳引起的温室效应及分离能源气体中的杂气(二氧化碳),二氧化碳的捕集与分离已经成为当今研究热点。

纳米纤维素具有比表面积大、机械强度高、可再生等优异性能,结合纳米材料和生物质材料的优势,利用纳米纤维素表面丰富的羟基基团制备绿色再生的高性能二氧化碳吸附剂具有重要研究意义。

本文采用化学和机械方法,以微晶纤维素和纸浆为原料,制备纳米纤维素晶体和纤丝,并对其形态及理化性质进行分析;将纳米纤维素悬浮液经悬浮滴定、叔丁醇置换和冷冻干燥等工艺制备纳米纤维素气凝胶,对比分析纳米纤维素晶体和纤丝制备气凝胶的特性变化规律;通过水浴加热处理将氨基硅烷改性剂接枝到纤维素链上,制得氨基功能化纳米纤维素气凝胶,测试其对二氧化碳吸附性能及对甲烷/二氧化碳混合气体的选择吸附能力,得出主要结论如下:(1)微晶纤维素经硫酸水解制备纳米纤维素晶体(CNC),呈短棒状,直径范围20-40nm,长度范围多在200-400nm,在强酸的作用下,部分表面的极性基团可能被取代,产生纤维素酯;纸浆经化学预处理结合机械研磨制备纳米纤维素纤丝(CNF),呈现长纤丝状,易团聚不易区分,直径范围50-70nm,长度范围多在1-2μm。

CNC和CNF的基本化学结构仍为纤维素Iβ型,结晶度都相较原料有不同程度的升高。

(2)以不同比例混合的CNC和CNF悬浮液为原料,经凝胶干燥得到纳米纤维素气凝胶。

通过分析表明:气凝胶内部呈现不规则的三维网络结构,N2吸脱附曲线均为Ⅳ型,且具有H1型滞留环;随着混合体系中CNF的增多,气凝胶形态由近似“球形”趋于近似“米粒状”,平均直径也随之升高。

当混合比为CNC:CNF=1:3时,气凝胶表现出比其他混合组份更优的性能,内部孔结构更加均匀,孔隙更加丰富,比表面积和压缩强度均最大。

(3)红外谱图上新吸收峰(NH2、NH、Si-O、Si-C等)的出现,以及X-射线光电子能谱上N、Si峰的出现可以证明:在纤维素链上成功接枝了氨基硅烷(AEAPMDS)。

高温高压条件下深部煤层气吸附行为

高温高压条件下深部煤层气吸附行为

高温高压条件下深部煤层气吸附行为赵丽娟;秦勇;Geoff Wang;吴财芳;申建【摘要】为了对深部煤层吸附特性进行分析,以鄂尔多斯盆地东部主要煤层为对象,展开4组不同温度条件下煤样的高压等温吸附实验。

从温度、压力、煤级等地质要素方面入手,研究较高温压条件下煤样的吸附特征。

同时,通过对比分析各地质因素对吸附行为的影响,比较深部煤层吸附行为与浅部煤层吸附行为的差异性。

结果表明:深部煤层的吸附特性主要受温度、压力的控制;高温条件下煤样对CH4的吸附量大大减少,且煤级、煤岩显微组分、灰分产率以及水分含量对吸附性能的影响已明显小于浅部煤层,温度、压力成为控制吸附量的决定因素。

在100℃条件下,吸附量到达某一压力后随着压力的增大煤样吸附量下降,分析认为由于在此温压下,随着压力的增加,吸附相与游离相气体的密度差逐渐减小,超临界吸附已不再符合Langmuir等温吸附模型。

%In order to analyze adsorption characteristics of deep coalbed, this paper studies the main coalbed of Eastern Ordos Basin and develops 4 groups of methane isothermal adsorption experiments of high pressure of the coal samples under different temperatures. By varying geological factors including temperature, pressure, and coal rank etc, we studied the adsorption characteristics under high temperatures and high pressures. Meanwhile, effects of geological factors on the adsorption behavior are analyzed by comparing results of different geologic factors, and the adsorption behaviors of deep coalbeds and shallow coalbeds. The results show thatthe adsorption characteristics of deep coalbeds is mainly influenced by temperature and pressure for deep coalbeds;The adsorption capacity ofcoal samples to CH4 is greatly reduced and the coal rank, coal macerals, ash content and moisture are less effective than the shallow coalbed on the adsorption property under high temperature conditions. So temperature and pressure become determinant factors in controlling the adsorption quantity. Adsorption capacities of the coal samples decrease along with the increase in pressure as the pressure reaches a certain value under 100℃according to the analyses, With the increase in pressure, the density difference of gas between the adsorbed phase and dissociative phase decreases gradually and Langmuir isothermal adsorption model is no longer applicable.【期刊名称】《高校地质学报》【年(卷),期】2013(000)004【总页数】7页(P648-654)【关键词】深部煤层气;吸附特征;高温高压【作者】赵丽娟;秦勇;Geoff Wang;吴财芳;申建【作者单位】中国矿业大学资源学院,徐州 221116;中国矿业大学资源学院,徐州 221116; 中国矿业大学煤层气资源与成藏过程教育部重点实验室徐州221116;School of Chemical Engineering,University of Queensland,St Lucia,QLD 4072,Australia;中国矿业大学资源学院,徐州 221116; 中国矿业大学煤层气资源与成藏过程教育部重点实验室徐州 221116;中国矿业大学资源学院,徐州 221116; 中国矿业大学煤层气资源与成藏过程教育部重点实验室徐州221116【正文语种】中文【中图分类】P618.13煤储层中,煤岩对CH4气体的吸附行为总是处在一定的温度、压力条件下。

英语单词eps是什么中文意思

英语单词eps是什么中文意思

英语单词eps是什么中文意思英语单词eps的中文意思[,i:pi:'es]原级:EP第三人称复数:EPsabbr. 每股收益; Earnings Per Share 每股利润网络解释1. 随速助力转向:一汽大众迈腾动力技术的几个亮点,此次交流会主要动力和底盘技术分两个板块,动力方面的介绍包括EA888系列发动机以及6速Tiptronic手自一体变速器,底盘部分此次讲解的是关于电动随速助力转向(EPS)和悬挂技术.2. 电动随速助力转向:制动力自动分配(EBD) 有车身稳定控制系统电子稳定程序(ESP),电动随速助力转向(EPS),刹车辅助3. 每股盈利:有没有人能算出浦发再融资前后, 每股盈利(EPS)的变化, 能算出来的人有重赏.有没有人能算出浦发再融资前后, 每股盈利(EPS)的变化, 能算出来的人有重赏.有没有人能算出浦发再融资前后, 每股盈利(EPS)的变化, 能算出来的人有重赏.4. 电控转向助力系统:电控可变进气系统,电控可变排量系统,电控可变气门正时和升程系统,电控电动风扇,电控空气弹簧等底盘电子系统防抱死系统(ABS),电控牵引力控制系统(TCS),电子控制制动系统(EBS),电控转向助力系统(EPS),电子制动力分配(EBD),5. eps:electronic power system; 电力系统6. eps:electronic power steering; 电动助力转向7. eps:electronic power steering system; 电动助力转向系统8. eps:emergency power supply; 备用电源英语单词eps的单语例句1. The Nepali workers are going there for the first time under the EPS.2. If the share price is set at 30 times the EPS, the shares would be priced at around 10 yuan per share.3. Her five studio albums and two EPs released since 2006 have all topped the Chinese music charts.4. Under the EPS, only the government can send the workers to South Korea.5. Approximately 220 million dollars is to be financed through China Eximbank with the remainder to be raised by EPS itself.英语单词eps的双语例句1. The composition of culture medium was optimized and the yield of EPS could arrive at2.5g/L when malt juice and domestic yeast powder as the industrial raw materials were used during the fermentation process.在多糖的分离纯化过程中比较了几种脱蛋白的方法,采用碱性蛋白酶与Sevage试剂相结合的'方法能较好的除去粗多糖中的杂蛋白。

多胺型聚苯乙烯树脂的合成及对Cu2+的吸附性能

多胺型聚苯乙烯树脂的合成及对Cu2+的吸附性能

CHEMICAL INDUSTRY AND ENGINEERING PROGRESS 2016年第35卷第10期·3258·化工进展多胺型聚苯乙烯树脂的合成及对Cu2+的吸附性能孟启,吕科翰,夏丰敏,倪梦燚(常州大学石油化工学院,江苏常州 213164)摘要:以聚苯乙烯树脂为起始原料,经氯乙酰化后与四乙烯五胺反应,合成了一种含四乙烯五胺功能基的多胺型聚苯乙烯树脂。

考察了溶剂、物料比、时间和温度等反应条件对树脂合成的影响,研究了树脂对Cu2+的吸附性能。

结果表明,合成反应在THF溶剂中室温即可顺利进行,所得树脂全交换容量为7.45mmol/g。

树脂对Cu2+的吸附可以用准二级动力学方程来描述,液膜扩散为吸附主要控制步骤,吸附符合Langmuir等温方程,为单分子层吸附,饱和吸附量为46.15 mg/mL。

对于Cu2+、Ni2+混合溶液,该树脂可以选择性吸附其中Cu2+。

关键词:四乙烯五胺;树脂;合成;吸附;铜离子中图分类号:O 632.6 文献标志码:A 文章编号:1000–6613(2016)10–3258–05DOI:10.16085/j.issn.1000-6613.2016.10.033Synthesis of polyamine-type polystyrene resin and its adsorption propertyfor Cu2+MENG Qi,LÜ Kehan,XIA Fengmin,NI Mengyi(Petrochemical Institute of Changzhou University,Changzhou 213164,Jiangsu,China)Abstract:A polyamine-type polystyrene resin with tetraethylenepentamine functional group was synthesized from polystyrene resin through chloroacetylation followed by the amination of tetraethylenepentamine. Effects of reaction solvent,mole ratio of raw materials,time and temperature were discussed. The adsorption property of the polyamine-type polystyrene resin for Cu2+ was also studied. The results show that the synthetic reactions can take place smoothly in THF at room temperature and the complete exchange capacity of the synthesized resin is 7.45 mmol/g. The adsorption processes of Cu2+ can be described by pseudo-second order kinetic equation. The main control step of resin adsorption for Cu2+ is governed by liquid film diffusion. The adsorption of Cu2+ belongs to the Langmuir adsorption model and was valid for single-layer adsorption. The saturated adsorption capacity of the synthesized resin toward Cu2+ is 46.15mg/mL. The Cu2+ can be removed selectively from the mixed solution of Cu2+ and Ni2+ by the synthesized resin adsorption.Key words:tetraethylenepentamine;resin;synthesis;adsorption;copper ion多胺结构对一些金属离子具有良好的螯合作用,通过多胺分子对聚合物的化学修饰可以制得多种具有特殊功能的新型材料[1-4],其中以多乙烯多胺为功能基的多胺型树脂具有结构稳定、用途广泛的特点,在合成技术研究和应用领域拓展等方面引起了人们广泛的关注[5-7]。

能源地质学专业术语中英文对照

能源地质学专业术语中英文对照
苔癣沼泽(sphagnum bog)
125
低位沼泽(flat bog,low moor)
126
中位沼泽(medium bog,medium swamp)
127
高位沼泽(raised bog,highmoor)
128
富营养沼泽(eutrophic mire)
129
中营养沼泽(mesotrophic swamp)
97
氯仿沥青A(chloroform bitumen A)
98
族组成(group composition)
99
饱和烃(saturated hydrocarbon)
100
芳烃(aromatic hydrocarbon)
101
胶质(colloid,pectin,colloid substance)
102
116
浅海(shallow sea)
117
泻湖(lagoon,lagune)
118
潮坪(tidal flat)
119
砂坪(sand flat)
120
泥坪(mud flat)
121
混合坪(mixed flat)
122
苔草沼泽(sedge mire)
123
木本沼泽(swamp,woody mire)
124
202
微粒体(micrinite)
203
粗粒体(macrinite)
204
菌类体(sclerotinite)
205
碎屑惰质体(inertodetrinite)
206
孢子体(sporinite)
207
角质体(cutinite)
195
均质镜质体(telocollinite)

Langmuir吸附等温式推导浅析

Langmuir吸附等温式推导浅析

Langmuir吸附等温式推导浅析姚晨曦;杨春信;周成龙【摘要】We presented three classical deduction methods of Langmuir adsorption isotherm,namely,adsorp-tion kinetics,adsorption thermodynamics,and DeBoen adsorption theory.Moreover,we mainly put forward a new deduction method——chemical reaction analogism,which introduced an adj ustable parameter ν1.Through the change ofν1,the deduced adsorption isotherm can describe monolayer adsorption as well as multimolecular layer adsorption.Whenν1is in different ranges,the shape of adsorption isotherm curve is the same as that of type Ⅰ,Ⅲ,and Ⅴ adsorption isotherms.We summarized and compared the core mechanisms of these deduction methods,and explored the substantive characteristics of gas-solid adsorption.%介绍了3种典型的 Langmuir吸附等温式推导方法,分别是吸附动力学、吸附热力学和德博尔吸附理论.重点提出了一种新的 Langmuir 吸附等温式推导方法——化学反应类比法,并引入可调参数ν1.推导出的吸附等温式通过ν1的取值变化既能描述单分子层吸附也能描述多分子层吸附,且当ν1在不同的范围内时,其吸附等温曲线形状与Ⅰ型、Ⅲ型、Ⅴ型吸附等温线形状相同.总结和比较了这几种推导方法的核心机理,探究了气固吸附的本质特征.【期刊名称】《化学与生物工程》【年(卷),期】2018(035)001【总页数】5页(P31-35)【关键词】Langmuir吸附等温式;吸附平衡;化学反应类比法【作者】姚晨曦;杨春信;周成龙【作者单位】北京航空航天大学航空科学与工程学院,北京100191;北京航空航天大学航空科学与工程学院,北京100191;北京航空航天大学航空科学与工程学院,北京100191【正文语种】中文【中图分类】O647.321940年,Brunauer S、Deming L S、Deming W E和Teller E等人将多种吸附等温线划分为5类,简称为Brunauer吸附等温线分类[1],如图1所示。

Ind. Eng. Chem. Res.2006; 45(14); 5066

Adsorption of Divalent Cadmium(Cd(II))from Aqueous Solutions onto Chitosan-Coated Perlite BeadsShameem Hasan,Abburi Krishnaiah,Tushar K.Ghosh,*and Dabir S.ViswanathNuclear Science and Engineering Institute,Uni V ersity of Missouri,Columbia,Missouri65211Veera M.Boddu and Edgar D.SmithUS Army Engineering Research and De V elopment Center(ERDC),Construction Engineering ResearchLaboratories,En V ironmental Process Branch(CN-E),Champaign,Illinois61826Chitosan-coated perlite beads were prepared in the laboratory via the phase inversion of a liquid slurry ofchitosan dissolved in oxalic acid and perlite to an alkaline bath for better exposure of amine groups(NH2).The NH2groups in chitosan are considered active sites for the adsorption of heavy metals.The beads werecharacterized by scanning electron microscopy(SEM)and energy-dispersive X-ray spectroscopy(EDS)microanalysis,which revealed their porous nature.The chitosan content of the beads was32%,as determinedusing a thermogravimetric method.The adsorption of Cd2+from an aqueous solutions on chitosan-coatedperlite beads was studied under both equilibrium and dynamic conditions in the concentration range of100-5000ppm.The pH of the solution was varied over a range of2-8.The adsorption of Cd2+on chitosan wasdetermined to be pH-dependent,and the maximum adsorption capacity of chitosan-coated perlite beads wasdetermined to be178.6mg/g of bead at298K when the Cd(II)concentration was5000mg/L and the pH ofthe solution was6.0.On a chitosan basis,the capacity was558mg/g of chitosan.The XPS data suggests thatcadmium was mainly adsorbed as Cd2+and was attached to the NH2group.The adsorption data could befitted to a two-site Langmuir adsorption isotherm.The data obtained at various temperatures provided a singlecharacteristic curve when correlated according to a modified Polanyi’s potential theory.The heat of adsorptiondata calculated at various loadings suggests that the adsorption was exothermic in nature.It was noted thata0.1N solution of HCl could remove the adsorbed cadmium from the beads,but a bed volume of approximatelythree times the bed volume of treated solution was required to completely remove Cd(II)from the beads.However,one bed volume of0.5M ethylenediamine tetra acetate(EDTA)solution can remove all of theadsorbed cadmium after the bed became saturated with Cd(II)during dynamic study with a solution containing100mg/L of cadmium.The diffusion coefficient of Cd(II)onto chitosan-coated beads was calculated fromthe breakthrough curve,using Rosen’s model,and was determined to be8.0×10-13m2/s.IntroductionCadmium plating is used for fasteners and other very-tight-tolerance parts,because of the dual qualities of lubricity at minimal thickness and superior sacrificial corrosion protection to many chemicals at high temperatures.Long-term exposure to cadmium can cause damage to the kidneys,liver,bone,and blood.Therefore,cadmium should be removed from waste streams before discharge into the environment.The removal of cadmium from wastewater is generally accomplished by precipitation with a hydroxide,carbonate,or sulfide compound.Also,several adsorbents s including activated carbon,recycled iron,novel organo-ceramic,hydrous cerium oxide,and low-cost adsorbents such as rice husk,date pits,fly ash,aerobic granular sludge,sewage sludge,tunable biopoly-mers,alginated coated-loofa sponge disks,surfactant-modified zeolites,porous poly(methacrylate)beads,red mud,goethite, perlite,and duolite s have been used for cadmium removal.1-17 The cadmium adsorption capacities of various adsorbents are summarized in Table1.Several researchers18-22have investigated chitosan as an adsorbent for removal of heavy metals,including cadmium from aqueous streams.Chitosan is a natural biopolymer,it is hydrophilic,and it has the ability to form complexes with metals.It is also a nontoxic,biodegradable and biocompatible material. According to Rorrer et al.,23chitosan flake or powder swells and crumbles,making it unsuitable for use in an adsorption column.Chitosan also has a tendency to agglomerate or form a gel in aqueous media.Although the amine and hydroxyl groups in chitosan are mainly responsible for adsorption of metal ions,these active binding sites are not readily available for sorption when it is in a gel or in its natural form.24Guibal et al.25noted that the maximum uptake of chitosan flakes was approximately half of that obtained with chitosan beads for molybdate.The adsorption capacity can be enhanced by spreading chitosan on physical supports that can increase the accessibility of the metal binding sites.Bodmeier et al.26noted that freeze-drying of chitosan gel produced particles with a high internal surface area,which boosted the metal binding capacity. Several attempts have been made to modify the structure of chitosan chemically,and its performance has been evaluated through the adsorption of heavy-metal ions from aqueous solutions.The amine and hydroxyl groups in chitosan allow a variety of chemical modifications.27Kawamura et al.28prepared a porous polyaminated chitosan chelating resin by introducing poly(ethylene amine)onto the cross-linked chitosan beads.The resultant beads showed high capacity and high selectivity for the adsorption of metal ions including cadmium.Hsien and Rorrer29investigated the adsorp-tion of cadmium on porous magnetic chitosan beads.They found*To whom correspondence should be addressed.Tel.:1-573-882-9736.Fax:1-573-884-4801.E-mail address:ghoshT@.5066Ind.Eng.Chem.Res.2006,45,5066-507710.1021/ie0402620CCC:$33.50©2006American Chemical SocietyPublished on Web06/15/2006that the adsorption capacities for1-and3-mm beads were518 and188mg Cd/g of adsorbent,respectively.They also investigated the effects of acylation and cross-linking of chitosan using gutaraldehyde.30They later noted that,although the cross-linked chitosan beads became more resistant to acid,the capacity of cross-linked chitosan for cadmium decreased significantly, compared to non-cross-linked beads.The adsorption of metal ions on gallium(III)-templated oxine type of chemically modified chitosan was reported by Inoue et al.31Chitosan cross-linked with crown ethers32,33showed improved adsorption capacity for cadmium and high selectivity for Ag(I)or Cd(II)in the presence of Pb(II)and Cr(III).Becker et al.34studied the adsorption characteristics of cadmium,along with other metals,on di-aldehyde or tetracarboxylic acid cross-linked chitosan.Although several attempts have been made to enhance the adsorption capacity of chitosan for cadmium and other metal ions through the cross-linking of chitosan,using various chemicals,the sorption capacity for metal ions decreased after the cross-linking of chitosan.Hasan et al.24noted that,by dispersing chitosan on an inert substrate(perlite)enhanced its adsorption capacity for Cr(VI).It is assumed that the active group,such as NH2,became more readily available.In this work,chitosan was dispersed on an inert substance to expose more-active sites for adsorption.Chitosan was coated on perlite,and the coated adsorbent was prepared as spherical beads.It is expected that the swelling and gel formation of chitosan can be reduced in this way,thus allowing regeneration and repeated use of the chitosan adsorbent in a column.The adsorbent was evaluated for cadmium by obtaining equilibrium adsorption data at different temperatures and pH.We also explored the regeneration of the adsorbent using dilute acid and the ethylenediamine tetra acetate(EDTA)solutions. Experimental SectionMaterials.Perlite(grade YM27)was donated by Silbrico Corporation(Hodgkins,IL).Chitosan and cadmium chloride were obtained from Aldrich Chemical Corporation(Milwaukee, WI).The chitosan used in this study was75%-85%deacety-lated and had a molecular weight of∼190000-310000,as determined from the viscosity data by Aldrich Chemical Corporation.All chemicals used in this study were of analytical grade.Oxalic acid,EDTA,and sodium hydroxide were pur-chased from Fisher Scientific Co.(Fairlawn,NJ).A stock solution containing5000mg/L of Cd(II)was prepared in distilled,deionized water using CdCl2.The working solutions of various Cd(II)concentrations were obtained by diluting the stock solution with distilled water.Preparation and Characterization of Chitosan-Coated Perlite Beads.Perlite powder(35mesh)was first soaked with 0.2M oxalic acid for4h.It then was washed with distilled water and dried in an oven for12h.Sixty grams of acid-washed perlite was mixed with30g of chitosan flakes in a beaker that contained1L of0.2M oxalic acid.The mixture was stirred for 4h while heating at313-323K(40-50°C)to obtain a homogeneous mixture.The spherical beads of chitosan,coated on perlite,were prepared via dropwise addition of the mixture into a0.7M NaOH precipitation bath.The beads were washed with deionized water to a neutral pH and freeze-dried for subsequent use.A detailed description of the bead preparation method has been discussed by Hasan et al.24The final diameter of the freeze-dried beads was∼2mm. The Brunauer-Emmett-Teller(BET)surface area of the beads was determined to be25m2/g,compared to3m2/g for the perlite particles.Most of the surface area of the beads is expected to be internal,because the external area is extremely small.The surface morphology of pure perlite changed significantly, following coating with chitosan,as indicated by scanning electron microscopy(SEM)micrographs of the beads.The SEM micrographs of the cross section of a bead also revealed the porous structure of the beads(Figure1a).A transmission electron microscopy(TEM)micrograph(Figure1b)of the beads showed that individual perlite particles were not necessarily coated with chitosan;rather,a group of particles were lumped together and coated by the chitosan film.Energy-dispersive X-ray spectrometry(EDS)microanalysis of the chitosan beads before and after their exposure to the cadmium solution confirmed the presence of Cd(II)in the interior of the beads. The EDS microanalysis shown in Figure2a exhibited peaks for aluminum and silicon,which are two major constituents of perlite.A strong peak at∼3.5keV for Cd on beads that were exposed to Cd(II)can be observed in Figure2b.In the EDS spectrum(Figure2b),a small peak for chlorine was also observed.The chlorine peak may have resulted either from the adsorption of chlorine on chitosan from the solution or fromTable1.Adsorption Capacity of Various Adsorbents for Cadmiumadsorbent pH adsorption capacity(mg/g)reference chitosan flakes 6.09.9Bassi et al.20magnetic chitosan beads1mm size 6.5518Rorrer et al.253mm size 6.5188Rorrer et al.25 non-cross-linked chitosan beads169Hsien et al.26N-acylated chitosan beads216Hsien et al.27cross-linked chitosan crown ethers 2.0-6.532.2Peng et al.29chitosan aryl crown ethers 6.039.3Yang et al.23glutaraldehyde cross-linked chitosan 3.0134.9Becker et al.31rice husk7.00.007Khalid et al.5perlite 6.6-6.70.64Mathialagan and Viraghavan16 diamine grafted chitosan crown ethers28.1Yang et al.30activated carbon 5.0 3.4An et al.21novel organo-ceramic 5.0212.8Gomez-Salazar et al.370.56modified corncorbs 4.89.0Vaughan et al.7Duolite GT-73resin 4.8105.7Vaughan et al.7Amberlite IRC-718resin 4.8258.6Vaughan et al.7Amberlite-200resin 4.8224.8Vaughan et al.7alginate-coated loofa sponge disks 5.088Iqbal and Edyvean11porous poly(methyl methacrylate)beads 6.024.2Denizli et al.13chitin 6.015.0Benguella and Benaissa22chitosan-coated perlite 5.0178.6present workInd.Eng.Chem.Res.,Vol.45,No.14,20065067the solution trapped inside the pores.However,it may be noted that some of the amine groups can undergo protonation in acidic solution,forming NH 3+,which is capable of adsorbing anions such as chlorine.Thermogravimetric analysis (TGA)of the beads indicated that the chitosan content of the bead was ∼32%.Chitosan started to decompose at ∼473K and was completely burned out at773K.The change of mass,as a function of temperature,is shown in Figure 3.Experimental ProcedureEquilibrium batch adsorption studies were performed by exposing the beads to aqueous solutions that contained different concentrations of Cd(II)ions in 125-mL Erlenmeyer flasks to a predetermined temperature.Approximately 0.25g of beads was added to 50mL of solution.The pH of the solutions was adjusted by adding either 0.1N sulfuric acid or 0.1M sodium hydroxide.The flasks were placed in a constant temperature shaker bath for a specific time period.Following the exposure of the beads to Cd(II),the solutions were filtered and the filtrates were analyzed for Cd(II)via atomic absorption spectrometry (AAS).The adsorption isotherm at a particular temperature was obtained by varying the initial concentration of Cd ions.The amount of Cd(II)adsorbed per unit mass of adsorbent (Q e )was calculated using the following equation:Results and DiscussionEffect of Surface Charge and pH on the Adsorption of Cd(II).The surface charge of the bead was determined via a standard potentiometric titration method in the presence of a symmetric electrolyte (sodium nitrate).The magnitude and sign of the surface charge was measured with respect to the point of zero charge (PZC).The pH at which the net surface charge of the solid is zero at all electrolyte concentrations is called the PZC.The pH of the PZC for a given surface is dependent on the relative basic and acidic properties of the solid 35and allows estimation of the net uptake of H +and OH -ions from the solution.The surface charge of the beads in the presence of 0.1M NaNO 3was determined in the following manner.36Four flasks,each containing 2g of chitosan-coated perlite beads,were exposed to 100mL of 0.1M NaNO 3solutions.The flasks were placed in a shaker for 24h at 125rpm.Samples from one of the flasks were titrated directly with 0.1M HNO 3,and samples from another flask were titrated with 0.1M NaOH.After the addition of the acid or base,the pH of the solution was recorded,after it was allowed to equilibrate.Titration was conducted over a pH range of 3-11.The beads were separated from the solutions of the remaining two flasks.The supernatants were titrated in a similar manner,but in the absence of beads.The net titration curve was obtained by subtracting the titration curve of the supernatant that was obtained without the presence of beads from the titration curve obtained with the beads.IntheFigure 1.(a)Scanning electron microscopy (SEM)micrograph of the cross section of the chitosan-coated perlite beads.(b)Transmission electron microscopy (TEM)micrograph of chitosan-coated perlite beads.The black spots represent perliteparticles.Figure 2.(a)Energy-dispersive X-ray spectrometry (EDS)microanalysis of chitosan-coated perlite beads,showing the presence of silicon and aluminum (platinum and silver were from the sputter coating of the sample for electrical contact).(b)EDS microanalysis of chitosan-coated perlite beads following exposure to CdCl 2.Figure 3.Thermogravimetric analysis (TGA)of chitosan-coated perlite beads:(-‚-‚-)freeze-dried beads and (s )oven-dried beads.Q e )(C i -C e )VM(1)5068Ind.Eng.Chem.Res.,Vol.45,No.14,2006absence of specific chemical interaction between the electrolytes and the surface of the bead,the net titration curves usually meet at a point that is defined as the pH PZC.Similar experiments were conducted with a0.05M NaNO3solution.No difference between the two titration curves obtained using two different ion strengths was observed.The surface charge was calculated from the following equation:37[H+]and[OH-]were calculated from the pH of the solution, after appropriate correction was made,using the activity coefficient.The activity coefficient was calculated using the Davis equation:38The results are shown in Figure4.The PZC value of the chitosan-coated perlite bead was determined to be8.5,which was similar to that reported by Jha et al.19for chitosan flake. However,Udaybhaskar et al.39reported a PZC value in the range of6.2-6.8for pure chitosan.The surface charge of chitosan-coated perlite bead was almost zero in the pH range of6-8.5. It may be noted that the p K a value of perlite was determined to be∼7.The protonation of the beads sharply increased at the pH range of3-4.5,making the surface positive.At pH<3.5, the difference between the initial pH and the pH after the equilibration time was not significant,suggesting complete protonation of chitosan.At higher pH(4.5-8.5),the surface charge of the bead slowly decreased,indicating slow protonation of chitosan on the bead.The PZC value of8.5and the behavior of surface charge of the bead could have been due to the modification of chitosan when coated on perlite,which makes it amphoteric in nature.Alumina and silica in perlite may have formed a bond with chitosan,according to the reaction shown in reactions5and6. At different ionic strengths,the surface charge of the bead was almost identical and the pH of the bead suspension did not increase when an electrolyte salt was added.The point to note from this figure is that PZC shifted toward6.5in the presence of Cd ions.As shown in Figure8(given later in this paper), CdCl2could hydrolyze to Cd(OH)2,releasing HCl,which would lower the solution pH.Also,H+ions are released during the adsorption of Cd2+ions by OH groups.As explained later,both the NH2and OH groups are expected to participate in the adsorption process.Their combined effect reduced the PZC value.To adsorb a metal ion on an adsorbent from a solution,it should form an ion in the solution.The types of ions formed in the solution and the degree of ionization are dependent on the solution pH.In the case of chitosan,the main functional group responsible for metal ion adsorption is the amine group(-NH2). Depending on the solution pH,these amine groups can undergo protonation to NH3+or(NH2-H3O)+,and the extent of protonation will be dependent on the solution pH.Therefore, the surface charge on the bead will determine the type of bond formed between the metal ion and the adsorbent surface. The effect of pH on the adsorption of Cd(II)by chitosan-coated perlite beads was studied by varying the pH of the solution over a range of2-8.The pH of the cadmium solutions was first adjusted over a range of2-8using either0.1N H2-SO4or0.1M NaOH and then chitosan-coated perlite beads were added.As the adsorption progressed,the pH of the solution increased slowly.No attempt was made to maintain a constant pH of the solution during the course of the experiment.The amount of cadmium uptake at the equilibrium solution concen-tration is shown for different initial pHs of the solution in Table 2,along with the final pH of the solution.The uptake of Cd(II) by chitosan beads increased as the pH increased from2to8. Although a maximum uptake was noted at a pH of8,as the pH of the solution increased to>7,cadmium started to precipitateσ0(C/m2))(Ca-Cb+[OH-]-[H+])FSa(2)logγi)-0.5109( I I+ I-0.3I)(3)I)0.5∑iCizi2(4)Figure4.Surface charge of chitosan-coated perlite beads in the presenceof CdCl2:([)0.1M NaNO3,(0)0.05M NaNO3,and(2)cadmiumsolution.Table2.Cadmium Uptake at Equilibrium at Various Solution pHat298Kconcentration at equilibriumof the liquid phase(mmol/L)uptake by thesolid phase(mmol/g)final pH ofthe solutionInitial pH of the Solution:20.3030.0285 2.10.5890.0607 2.11.6070.12502.43.4820.1964 2.56.9640.3214 2.6Initial pH of the Solution:4.50.0890.036 4.50.4020.098 4.61.2500.196 4.63.0360.286 5.06.6960.424 4.9Initial pH of the Solution:60.2250.080 6.20.4020.143 6.21.1600.268 6.32.6790.375 6.56.1600.536 6.6Initial pH of the Solution:80.0890.0898.00.3200.1618.11.1600.3218.22.7700.4468.35.9400.5808.6Ind.Eng.Chem.Res.,Vol.45,No.14,20065069out from the solution.Therefore,experiments were not con-ducted at pH >8.0.The increased capacity at pH >7may be a combination of both adsorption and precipitation on the surface.It is concluded that the beads had a maximum adsorption capacity at a pH of ∼6,if the precipitated amount is not considered in the calculation.The amine group of the chitosan has a lone pair of electrons from nitrogen,which primarily act as an active site for the formation of chitosan -metal-ion complex.As mentioned previously,at lower pH values,the amine group of chitosan undergoes protonation,forming NH 3+,which leads to an increased electrostatic attraction between NH 3+and the sorbate anion.Cadmium in an aqueous solution is hydrolyzed with the formation of various species,depending on the solution pH.Moreover,Cd 2+,which is the main hydrolyzed cadmium species in the pH range of 5-7appear in the form of Cd(OH)+,Cd(OH)20,and Cd(OH)3-.Among them,Cd 2+is the predominant species in the solution within this pH range.The fraction of negatively charged hydrolysis products in the solution increases as pH increases.Various hydrolysis reactions are given by Reed and Matsumoto 40and Baes and Mesmer.41Chitosan can form chelates with cadmium ions (Cd 2+)with the release of H +ions.A chelate formation may require the involvement of two or more complexing groups from the molecule.The Cd ion may seek two or more amine groups from chitosan to form the complex.This should normally reduce the pH of the solution.Kaminiski and Modrzejewska 42suggested that the increase in pH may be attributed to the exchange of released H +ions between the surface of the bead and the solution.In the case of chitosan,the protonation of NH 2groups occurs at a rather low pH range.The fact that the pH of the solution increased as the adsorption progressed suggests that Cd(II)formed a covalent bond with the NH 2group.The two NH 2groups could come from two different glucosamine residues of the same molecule,or from two different molecules of chitosan.Jha et al.19compared the stability constants for ammonia and amino complexes with those for chloro complexes of cadmium and noted that the formation of covalent bond with amine nitrogen is the more-preferred reaction.It was noted that the present adsorbent can adsorb 4.98mmol Cd/g of chitosan at 298K when the Cd(II)concentration was 5000mg/L and the pH of the solution was 6.0.The NH 2groups are the main active sites for cadmium adsorption.As can be seen from Figure 8(presented later in this paper),two NH 2groups will benecessary for the adsorption of one Cd ion,because the concentration of NH 2on chitosan is ∼6.9mmol/g.The maximum capacity for cadmium should be ∼3mmol/g.Because the maximum capacity obtained experimentally is 4.98mmol/g,other sites such as CH 2OH,OH,or O groups are also involved in adsorbing cadmium.At pH <2.0,NH 3+starts to hinder the adsorption on the beads,resulting in a further decrease in the capacity.As the pH increases,the deprotonation of amine groups may occur,resulting in a decrease of competition between proton and metal species for surface sites of the bead.21Most of the adsorbents investigated by previous reseahers 16,18,19,36,41did not adsorb any Cd(II)at pH <4,except the present chitosan-coated perlite.It may be noted from Figure 5that both pure perlite and chitosan did not adsorb any cadmium at pH <4.The chitosan-coated perlite beads showed two distinct regions in the pH curve.It seems that,between pH 2and 4.5,one site (mainly NH 2)was most active and at pH >4.5,another site (OH groups)became active for the adsorption of cadmium.Perlite may have provided more-energetic active sites for the adsorption and prevented protonation of amine groups and thus enhanced the adsorption from a more-acidic solution,compared to other adsorbents.Note that pure perlite had an almost-negligible adsorption capacity for Cd(II),as shown in Figure 9(presented later in this paper).Mathialagan and Viraghavan 16also observed a similar capacity for Cd(II)on perlite.The XPS analysis of beads before and after the adsorption of Cd(II)was used to gain a better understanding of adsorption sites onto which Cd(II)was adsorbed.The XPS data were obtained using a KRATOS model AXIS 165XPS spectrometer with nonmonochromatic Mg X-rays (h ν)1253.6eV),which were used as the excitation source at a power of 240W.The spectrometer was equipped with an eight-channel hemispherical detector,and the pass energy of 5-160eV was usedduringFigure 5.Effect of pH on cadmium uptake by pure perlite (initial concentration of 1mg/L;data from ref 16),pure chitosan (initial concentra-tion of 2mg/L;data from ref 19),and chitosan-coated perlite beads (initial concentration of 100mg/L;data from thiswork).Figure 6.X-ray photoelectron spectroscopy (XPS)survey scans for chitosan flakes (top spectrum)and chitosan-coated perlite beads (bottom spectrum).The inset in top spectrum indicates the C 1s position in the chitosan flake,whereas the inset in bottom spectrum indicates the C 1s position in chitosan-coated perlite beads.5070Ind.Eng.Chem.Res.,Vol.45,No.14,2006the analysis of samples.Each sample was exposed to X-rays for the same period of time and intensity.The XPS system was calibrated using peaks of UO 2(4f 7/2),whose binding energy was 379.2eV.A 0°probe angle was used for analysis of the samples.Figures 6a and 6b show the peak positions of carbon,oxygen,and nitrogen present in chitosan flakes and chitosan-coated perlite beads,respectively.The C 1s peak observed at 284.3eV (with a full width at maximum height (fwmh)at 3.27)showed two peaks on deconvolution:one for C -N at 284.3eV and the other one for C -C at 283eV.In chitosan-coated perlite beads,the C 1s peak was observed at 283.5eV,compared to 284.3eV for chitosan flakes.Chemical shifts are considered significant when they exceeded 0.5eV.44The fwhm for all peaks from chitosan-coated perlite beads was observed to be wider than that of chitosan flakes.This indicates that functional groups of chitosan (-NH 2,-OH)may have formed a complex through cross-linking with a constituent of perlite during the coating process,as shown in reactions 5and 6.One of the objectives for coating chitosan on an inert substrate was to expose more NH 2groups on the surface,which are considered active binding sites for chitosan.The nitrogen concentration,as determined from the N 1s peak on chitosan-coated perlite beads,was almost twice that calculated for chitosan flakes.It may be noted that perlite has no nitrogen-containing groups;therefore,the nitrogen in that sample came entirely from chitosan.The high nitrogen content on the bead,as shown in the spectra,was due to the better dispersion of chitosan on the perlite surface.Table 2shows the surface elemental analysis,as determined from the peak area,after correcting for the experimentally determined sensitivity factor ((5%).To understand the binding of Cd(II)to the active sites on chitosan,beads exposed to 100mL of a 1000mg/L cadmium solution at pH 5was used for analysis via XPS.After 24h of exposure,the beads are removed from the solution and dried at room temperature.The dried beads were then analyzed by XPS.A portion of the beads was kept in desiccators and was again analyzed by XPS after approximately one month.The results are shown in Table 3.Note,from the XPS spectrum,that the C 1s and O 1s peaks shifted by 0.5eV,whereas the N 1s peak shifted by 1.78eV.These shifts are a result of the chemical interaction of Cd(II)with the functional groups in chitosan.The larger shift on the N 1s peak is an indication that Cd(II)was strongly bound to the NH 2groups on chitosan.As shown in Figure 7,chitosan beads that were analyzed immediately after 24h of exposure showed predominant bands for Cd 3d,O 1s,and C 1s peaks,whereas N 1s,Cd 3p,Cd 4d,and Auger electrons had smaller bands.For cadmium,the most intense peaks were observed for Cd 3d 5/2at ∼405eV and Cd 3d 3/2at 404eV,which suggests that most of the adsorbed cadmium was on the surface of chitosan.The XPS analysis of beads that were removed from the solution and dried but were analyzed after one month showed a low-intensity peak by theside of the main peak of Cd 3d,which indicates the adsorption of hydrolysis products of cadmium,such as Cd(OH)2.The ratio of Cd/O and Cd/N decreased significantly (particularly the Cd/N ratio).This decrease may be attributed to further transport of cadmium by diffusion onto the inner core.Based on the XPS analysis and the adsorption data at various pH,the adsorption mechanism that was hypothesized is shown in Figure 8.Equilibrium Adsorption Results.As mentioned in the previous section,chitosan-coated beads provided the best capacity for Cd(II)ions at pH 6.0without any precipitation of Cd(II)from the solution.Therefore,the equilibrium studies at various temperatures were performed at this pH.The equilibrium adsorption data at pH 6.0and in the temperature range of 293-313K for Cd(II)are shown in Figure 9.Type I isotherms were obtained at all temperatures.Although the Langmuir equation provided a reasonable fit to the equilibrium adsorption data,the pH dependence could not be correlated using this model.The pH dependence of the metal adsorption can be explained by the competitive adsorption of metal ions and H +ions as follows:where q m is the maximum adsorption amount of metal ions (expressed in terms of mol/g),andIn Figure 5,the pH-dependent cadmium adsorption curve ofTable 3.Absolute Binding Energy (BE)for the Elements Present in the Beads Obtained from X-ray Photoelectron Spectroscopy (XPS)AnalysisCNOCd 3d sample aBE (eV)atomic weight(%)BE (eV)atomic weight(%)BE (eV)atomic weight(%)BE (eV)atomic weight(%)Cd/NCd/O1283.067.25397.5 5.10530.527.072283.557.61397.5 3.91530.528.113283.562.95398.0 3.45530.519.9404 6.07 1.7590.3054284.054.31398.03.80530.531.34404 1.130.2970.036aSample legend:1,chitosan flake;2,chitosan-coated perlite (CP)beads;3,CP beads that were separated from the solution after 24h of exposure to cadmium solution,dried,and analyzed immediately after drying;and 4,CP beads that were separated from the solution after 24h of exposure to cadmium solution and dried,and then the dried beads were kept in a desiccator and analyzed after 1month.Figure 7.Survey scan of chitosan-coated perlite beads exposed to CdCl 2.Inset shows a Cd 3d spectrum of beads exposed to CdCl 2.(Beads were exposed to the cadmium solution for 24h,and XPS analysis on dried beads was conducted immediately.)-SH T -S +H +(K H )(7)-S +M T -SM(K M ,where M is a metal ion)(8)q )q m R K m [M]1+R K m [M](9)R )K H K H +[H +]Z (10)Ind.Eng.Chem.Res.,Vol.45,No.14,20065071。

典型吸附模型的非线性和线性拟合对比分析


ΔH 为焓变ꎬJ / molꎻR 为气体常数ꎻK d 为热力学平衡
常数ꎮ
(2) 线性模型
对非线性模型经过整理ꎬ得 lnK d =
ΔS ΔH


R RT
3 吸附等温线模型的非线性拟合和线性
拟合结果对比
按照试验方法进行吸附等温试验ꎬ试验结果
及吸附模型线性拟合所需的数据ꎬ见表 1ꎬ将表 1
第一列数据输入到软件中ꎬ对 Langmuir 和 Freun ̄
Keywords: Adsorption Modelꎻ Nonlinear Fittingꎻ Linear Fittingꎻ Sandꎻ Ammonia Nitrogen
CLC number: X522
反应溶液中吸附过程的模型有很多ꎬ如经典
典的模型在研究溶液的吸附作用时具有非常大的
的 Langmuir 和 Freundlish 吸附等温线模型ꎬ还有
fitting Butꎬ the situation of fitting results for pseudo - second - order adsorption kinetics model and Van’ t Hoff model was
different The correlation coefficient of linear fitting was greater than or equal to nonlinear fitting correlation coefficientꎬ and the
速率常数ꎬh - 1 ꎮ
(2) 线性模型
对非线性模型经过整理可得 ln(qe - qt ) = lnqe -
k1 tꎬ式中 qe 为未知量ꎬ但可由试验结果得出ꎮ

磺酸树脂催化环己酮肟液相贝克曼重排反应

D-72磺酸树脂催化环己酮肟液相贝克曼重排制己内酰胺游奎一1,曾珍1,王良芥1,刘平乐1,吴剑1,李松1,尹笃林2,罗和安1 (1. 湘潭大学化工学院;教育部化工过程模拟与优化工程研究中心,湖南湘潭411105;2. 湖南师范大学化学化工学院,湖南长沙410081)摘要:在以二甲亚砜作溶剂,以D-72固体磺酸树脂为催化剂的两相体系中,实现了由环己酮肟液相贝克曼重排制备己内酰胺的反应。

主要考察了环己酮肟在固体酸催化剂上的吸附热力学规律以及溶剂、反应温度、反应时间、催化剂用量以及催化剂的重复使用性等因素对重排反应的影响。

结果表明,环己酮肟在磺酸树脂上的等温吸附过程符合Langmuir吸附模型,吸附等温线可用Langmuir等温方程和速率方程来描述。

在二甲亚砜溶剂中,当反应温度在130 ℃,催化剂用量为0.5 g(催化剂:环己酮肟=1:2(质量比))的条件下反应6小时,环己酮肟的转化率高达100%,己内酰胺的选择性为86.2%,主要副产物为环己酮。

该法对环境无害,反应条件温和,催化剂容易分离和可重复使用等优点。

关键词:D-72磺酸树脂;二甲亚砜;液相贝克曼重排;环己酮肟;己内酰胺中图分类号: O643. 32文献标识码: ALiquid Phase Beckmann Rearrangement of Cyclohexanone Oxime into ε-Caprolactam Catalyzed by D-72 Sulfonic Acid ResinYOU Kui-yi1, ZENG Zhen1, WANG Liang-jie1, LIU Ping-le1, WU Jian1, LI Song1,YIN Du-lin2, LUO He-an1*(1.College of Chemical Engineering, Xiangtan University; Engineering Research Center of Chemical ProcessSimulation & Optimization of Ministry of Education, Xiangtan 411105, China;2.College of Chemistry and Chemical Engineering, Hunan Normal University, Changsha 410081, China)Abstract: The liquid phase Beckmann rearrangement of cyclohexanone oxime into ε-caprolactam was successfully developed by using D-72 sulfonic acid resin as catalyst and dimethylsulfoxide as solvent in a two-phase system. The effects of solvent, reaction temperature, reaction time and amount of catalyst on the rearrangement of cyclohexanone oxime were examined. The results indicate that the adsorption behavior of cyclohexanone oxime on sulfonic acid resin accords with Langmuir adsorption model and can be described by Langmuir isotherm and speed equation. And the conversion of cyclohexanone oxime can reach 100% with 86.2% of selectivity to ε-caprolactam when the reaction was carried out at 130 ℃ for 6 h in dimethylsulfoxide solvent (m (catalyst): m (oxime) =1:2 (mass ratio)). This catalytic system involved is environmentally harmless, mild reaction conditions, and the catalyst can be conveniently recovered for recycled use.Key words: D-72 sulfonic acid resin; Dimethylsulfoxide; Liquid phase Beckmann rearrangement; Cyclohexanone oxime; ε-Caprolactam第一作者: 游奎一(1979-), 男, 博士, 副教授。

吸附法常见模型

实验汇报:预负载饱和:2.68mmol/gQC释放:不同比例:Pb:NPQ -N PIR等温线模型:1)The Langmuir isotherm model 几点假设: 单层吸附位点吸附能力相同、分布均匀;ee e bC C bQ Q +=10其简化形式为:bQ Q C Q C e e e 001+=11bC R L +=Qe 是平衡时吸附量mmol/g ; Q0是单层饱和吸附量;b 是吸附常数,代表吸附亲和力; Ce 是平衡时溶液浓度mmol/LR L 是分离系数,反应吸附类型。

大于1,非优惠;=1是线性吸附;在0-1之间为优惠吸附。

2)The Freundlich modelAssumes a heterogeneous adsorption surface with sites having different adsorption energiesKf 是吸附平衡常数,which indicates the adsorption capacity and represents the strength of the adsorptive bondn is the heterogenity factor (不均匀系数) which represents the bond distribution 一般认为n 为2-10时容易吸附即优惠吸附;n 小于0.5时难于吸附。

3)The Dubinin-Redushckevich (D-R ) isothermit does not assume a homogeneous surface or constant adsorption potential.Q 即Qe ,平衡吸附量k is a constant related to the adsorption energy (mol2 kJ-2) Qm is the maximum adsorption capacity (mol g-1) ε is the Polanyi potential (J mol-1)通过Q和Ce可以拟合出k和Qmthe mean free energy of adsorption (E) was calculated from the k valuesE =8 - 16 kJ mol-1, the adsorption process is triggered by ion exchangeE <8 kJ mol-1, physical forces such as Van der Waals and hydrogen bonding may affect the adsorption mechanismE>16 kJ mol-1 , the adsorption process is of a chemical nature(from:Sep. Sci. Technol. 37 (2002) 343-362.)4)Frumkin equationθ is the fractional occupation (θ = Qe/Qm; Qe is the adsorption capacity inequilibrium (mg g-1)Qm is the theoretical monolayer saturation capacity (mg g-1) which is determined by D–R isotherm equation)The constant k is related to adsorption equilibriumThe positive a values indicate that there is attractive interaction between the heavy metal ions. The different a values are attributed to differences in the intensity of the interactions between heavy metal ions.The negative values of G o意味着吸附过程为自发行为、优惠吸附。

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Journal of Catalysis245(2007)415–427/locate/jcatA three-site Langmuir adsorption model to elucidate the temperature,pressure,and support dependence of the hydrogen coverageon supported Pt particlesYaying Ji a,1,Vincent Koot a,Ad M.J.van der Eerden a,Bert M.Weckhuysen a,Diek C.Koningsberger a,∗,David E.Ramaker ba Group of Inorganic Chemistry and Catalysis,Department of Chemistry,Utrecht University,PO Box80083,3508TB Utrecht,The Netherlandsb Chemistry Department,George Washington University,Washington,DC20052,USAReceived2August2006;revised24October2006;accepted30October2006Available online5December2006AbstractThe three-site adsorption model,previously developed to describe H adsorption on small Pt particles,was used to gain insight into dependence of hydrogen coverage on temperature,pressure,and support ionicity.The three sites,in order of decreasing Pt–H bond strength,involve H in an atop,a threefold,and an ontop Pt site.The ontop site designates H bonded in an atop site surrounded by occupied threefold sites(hence referred to as ontop site).The model includes an emptying of the H atop sites into H threefold sites with increasing H pressure to reduce lateral interactions. Hydrogen chemisorption on an acidic Pt/H-USY and a basic Pt/NaY and TPD results on a acidic Pt/H-LTL and basic Pt/K-LTL are modeled using a Langmuir isotherm for each H site.The H/M data can be directly compared with Pt L2,3XANES results on the same samples.A new analysis method(Delta XANES technique)using the difference in the absorption coefficient, μ=μ(H/Pt)−μ(Pt),allows an in situ spectroscopic determination of the type of H adsorption site and H coverage.The adsorption enthalpies( H’s)for the atop,threefold,and ontop sites are found to be highly dependent on the support ionicity,increasing for ionic(basic)supports consistent with previous results.The calculations using the three-site model confirm that the support-induced changes in the Pt–H bond strength produce dramatically different H coverages and dominant adsorption sites at catalytic reaction temperatures and pressures.Depending on uptake versus desorption of H,a hysteresis is found in the atop to threefold site rearrangement,believed to result from a requirement for collective rearrangement involving an entire domain or island of H on the surface.©2006Elsevier Inc.All rights reserved.Keywords:Three-site hydrogen adsorption model on Pt;Metal–support interaction;Ontop/n-fold/atop hydrogen adsorption sites;Temperature/pressure and support dependence of hydrogen coverage1.IntroductionH adsorption on supported Pt particles is critical in supported noble metal catalysts,which are widely used in commercially important reactions,including hydrogenation,naphtha reform-ing,isomerization reactions,and electrocatalysis such as that taking place in a fuel cell[1].The stimulus for the current work *Corresponding author.E-mail address:d.c.koningsberger@chem.uu.nl(D.C.Koningsberger).1Present address:Center for Applied Energy Research,University of Ken-tucky,2540Research Park Drive,Lexington,KY40511,USA.is recent advances in X-ray absorption spectroscopy(XAS), which now enable XAS to provide H binding site information in situ on supported Pt particles both in the gas phase and in an electrochemical cell[2].These recent advances arise from new data analysis procedures,rather than new experimental tech-niques.A new analysis method(Delta XANES technique)has been developed that makes use of the difference in the X-ray absorp-tion coefficient, μ=μ(H/Pt)−μ(Pt),withμ(H/Pt)the X-ray absorption in the presence of andμ(Pt)that in the absence of chemisorbed hydrogen.Teliska et al.[3]used this Delta XANES technique to examine Pt particles supported on carbon0021-9517/$–see front matter©2006Elsevier Inc.All rights reserved. doi:10.1016/j.jcat.2006.10.028416Y.Ji et al./Journal of Catalysis245(2007)415–427 (Pt electrodes),and Oudenhuijzen et al.[4]studied Pt supportedon Al2O3or dispersed in LTL and Y zeolite(Pt catalysts).ThePt L3XANES data of the sample in vacuum or at0.5V in anelectrochemical cell(i.e.,when the Pt surface is relatively freeof H and other adsorbates)are subtracted from the data obtainedafter chemisorption of hydrogen: μ=μL3(H/Pt)−μL3(Pt).The signature of this difference spectrum( μ)is compared with μacquired from a similar procedure applied to theoret-ical results obtained with the help of full multiple scattering ab initio calculations using the FEFF8code[5]to identify specific H adsorption sites on the surface of the Pt particles.These re-sults have been combined with density functional calculations using the ADF code[6]to fully interpret the experimental data.After a thorough analysis of hydrogen TPD data in the liter-ature comparing Pt(111)data,stepped surfaces,polycrystalline Pt,and large supported Pt particles(>5nm),Teliska et al.[3] identifiedfive different features in the hydrogen TPD curves for polycrystalline Pt,each representing a specific H adsorption site.Five features were also found in the current voltage(CV) curves obtained in an electrochemical cell using3–5nm Pt clus-ters supported on carbon as electrode material.Teliska et al.[3] used the Pt L3Delta XANES signatures on these latter clusters to identify thefive adsorption sites.These adsorption sites in or-der of increasing adsorption bond strength, G= H−T S, are ontop H near edges,n-fold H and delocalized H on the faces,and n-fold H and delocalized H near Pt edges,as sum-marized on the left side of Fig.1.Because both the applied potential and temperature can be varied in electrochemistry,the H and S for H adsorption in the two primary absorption sites(n-fold on faces and n-fold near edges)have been obtained from the CV curves[7].The H values obtained from these studies are comparable to those obtained from hydrogen TPD studies in the gas phase and from theoretical calculations.This strongly suggests that the H binding sites in an electrolyte and in the gas phase are comparable[8].By using the Delta XANES technique described above and applying DFT calculations on Pt model clusters,the influence of the acid/base properties of the support on the chemisorption properties of hydrogen on intermediate Pt particles(2.5>d> 1nm)has been elucidated by Oudenhuijzen et al.[4].These authors showed that the Pt–H bond strength is greater on ionic supports(basic oxides with electron-rich O atoms),resulting in a higher hydrogen coverage compared with covalent supports (acidic oxides with electron-poor O atoms).Depending on the temperature and ambient H2pressure,on the Pt n-fold sites H is found near cluster edges and/or corners on basic supports and in the atop position near cluster edges/corners,with lower adsorption energy,on acidic supports.Based on these results, a three-site model has been proposed[4]for intermediate-sized Pt clusters in the gas phase,with the binding energy increasing in the following order:ontop H and n-fold H on faces,n-fold near the edges,and atop;these are summarized in the center of Fig.1.The temperature,hydrogen pressure,and ionicity of the support determine the H coverage of each site and consequently which type of site is available for hydrogen dissociation.The results obtained on Pt(111)single-crystal surfaces and the large Pt particles(3–5nm)supported on carbon usedas Fig.1.Left side and center:schematic illustration of the5or3different H bind-ing sites identified previously as discussed in the text,and how they correlatebetween large and intermediate size particles.Right side:schematic illustrationof a simple Frumkin isotherm model which assumes G= G0+gθ,where g represents the decrease in Gibbs free energy with increasing coverage due tolateral interactions(···),and three-site model utilized in this work which as-sumes a Langmuir isotherm(i.e.,non-changing G with coverage)but withthree different bonding sites as noted(—).The arrows in all cases indicate theatop/n-fold rearrangement that arises due to lateral interactions. electrodes[3](see the left side of Fig.1)can be correlated with the data obtained on smaller supported Pt particles(2.5>d> 1nm)(see center of Fig.1),such as those used in catalysis[4]. The changeover of the strongest bonding site from delocalized H as found on Pt(111)single crystals and Pt/C electrodes to atop H as detected on the much smaller Pt particles with sharper cor-ners is due to the decreasing Pt coordination at these corners[4]. Delocalized H arises when the atop,bridged,and n-fold sites have comparable energy as on single crystal surfaces,so the H can decrease its zero-point vibrational energy by delocalizing over these three sites.Near sharp corners as on small metal par-ticles,the atop sites have increased binding energy,so the H prefers the atop sites.Direct experimental proof for the influence of the support ionicity on the H coverage has been obtained from hydrogen chemisorption experiments on Pt particles dispersed in zeo-lite NaY,where the ionicity of the support oxygen is tuned by exchange of Na with different types of cations(H+,Mg2+, La3+)[9].DFT calculations[4,10]show that the Pt sp orbitals are important for H bonding,and that the rearrangement of the Pt6s and6p interstitial bond orbitals(IBO)with change of the support ionicity can explain these different Pt–H bonding prop-erties.In this work we correlate Pt L2,3XANES data,H/M chemisorption,and TPD data to elucidate the changes of H coverage on Pt particles(average Pt particle size,0.8–1.2nm) as a function of pressure,temperature,and support ionicity (Pt/H-USY vs Pt/NaY and Pt/H-LTL vs Pt/K-LTL).A three-site adsorption model,developed using a Langmuir isotherm and three different H adsorption sites(as summarized in the right side of Fig.1),will be shown to account for the variation in coverage with change in T,P,and support conditions as de-scribed above.Tofit the H/M data,a H2physisorption isothermY.Ji et al./Journal of Catalysis245(2007)415–427417also may be included.The three H adsorption sites are,in order of increasing bond strength:ontop/n-fold faces,n-fold edges, and atop H(see the center of Fig.1).The n-fold face and on-top H sites are merged into one type,denoted simply as ontop bonded H,and the n-fold edge(n f e)simply as n f in this work. The results from this work indicate that three adsorption sites with three different G values and Langmuir isotherms can ac-count for the changes in H coverage as a function of pressure, temperature,and support ionicity.The ramifications of these observations for the catalytic properties of supported Pt parti-cles will be discussed.2.Methods2.1.ExperimentalDetails about the preparation of the Pt/LTL catalysts,com-position of the supports,TPD experiments,and EXAFS data collection and analysis are given elsewhere[11–13].The K/Al molar ratios of the acidic Pt/H-LTL and basic Pt/K-LTL were 0.34and1.05,respectively.The average Pt–Pt EXAFS coordi-nation number was around4,pointing to an average Pt particle diameter of0.8nm.2.1.1.Preparation and characterization of the Pt particles dispersed in Y zeoliteThe NaY and NH4-USY(LZY84)supports were obtained from commercial zeolite powders[9].Highly dispersed Pt par-ticles were introduced inside the zeolite pores by applying a very careful synthesis procedure to obtain a narrow particle size distribution.The preparation and characterization of both cata-lysts is described elsewhere[9].In short,an aqueous solution of Pt(NH3)4(NO3)2(Aldrich),containing an amount of Pt lead-ing to a1wt%loading in the zeolite,was injected on the dry support in static vacuum.The sample was then heated with a ramp of0.2◦C/min from150to300◦C and calcined at300◦C for1h.For Pt/H-USY,afinal temperature of350◦C was used for calcination to remove ammonia from the acid sites of NH4-USY to obtain Pt/H-USY.After calcination and reduction at 300◦C,the sample was cooled to room temperature inflowing hydrogen,flushed with a highflow of N2,andfinally passivated by adding a smallflow of O2into theflowing N2.In an earlier study,similar samples were characterized by HRTEM,hydrogen chemisorption at RT and EXAFS[9].The average Pt particle size for Pt/H-USY and Pt/NaY was1.26 and1.14nm,respectively,determined from the HRTEM data by computer analysis of the photographs.The dispersion was calculated from the averaged Pt particle size as0.80and0.83, ing the H/M data and the calculated dispersion, it was possible to determine the number of adsorbed hydro-gen atoms per surface Pt(H/Pt s)[9].This value was much higher for the Pt/NaY sample with a higher ionicity of the support oxygen atoms than for Pt/H-USY,as mentioned in Sec-tion1.The Pt/NaY sample used in this work was prepared similarly but was not exactly the same as that used previ-ously[9].2.1.2.TPDH2TPD experiments were performed on the Pt/LTL cata-lysts after initial reduction in H2at300◦C.The desorption was programmed at a rate of10◦C/min to700◦C inflowing N2. The H2and N2were purified by passing them over oxygen and hydrocarbon traps.Cryogenic traps containing5Åmolecular sieve were placed directly before and after the furnace for water trapping.Desorbed gases were monitored by a thermal con-ductivity detector and periodically checked by independent gas chromatographic or mass spectrometry analyses for H2.Full de-tails have been provided previously[12].2.1.3.Hydrogen chemisorptionHydrogen chemisorption measurements were performed in a conventional static volume apparatus(Micromeritics ASAP 2010C).The samples werefirst dried under evacuation at 100◦C overnight,then reduced in pure H2at300◦C for1h (ramp rate,5◦C/min).The samples were evacuated at this tem-perature for0.5h,and then cooled in vacuum to the temperature at which the H2adsorption was to be determined.The absolute amount of adsorbed H2is determined from the decrease in pres-sure when adding afixed volume of H2to a known volume containing a known amount of catalyst.The H/Pt ratios are ob-tained based on the adsorbed amounts of hydrogen determined with this isotherm by extrapolation of the linear part to zero pressure.After thefirst H2adsorption isotherm was obtained, the sample was evacuated at the same temperature for10min to remove weakly adsorbed H2,after which H adsorption was performed again to obtain the second isotherm.After the sec-ond isotherm was obtained,the sample was evacuated at300◦C once again,before hydrogen adsorption was carried out at the next elevated temperature via the same procedure.In this way, a series offirst and second H isotherms as a function of temper-ature were obtained.The following series of temperatures was used:35,75,100,150,and200◦C.Thefirst hydrogen adsorption isotherm obviously reflects the total H adsorption(i.e.,physisorption and chemisorption)on the samples.Evacuation removes a fraction of the adsorbed H (weakly chemisorbed H and physisorbed H2),leaving only the strongly bound hydrogen still on the surface of the Pt parti-cle.Thus,the second isotherm reflects the additional weakly chemisorbed and physisorbed H which adsorbs at each T.The difference between these two isotherms is relatively constant with P,as shown elsewhere[9],and reflects the amount of strongly bound H remaining on the surface at the temperature of the H/M experiment and the vacuum pressure used before be-ginning the second isotherm.We use the difference between the first and second isotherms to obtain information on the strongly bound H in NaY zeolite.2.1.4.XAFS spectroscopyX-ray absorption data were collected at the Pt L3and L2edge using beamline X1.1of the HASYLAB synchrotron (Hamburg,Germany)equipped with a Si(311)crystal.The monochromator was detuned to50%of maximum intensity.All measurements were done in transmission mode using ion cham-bersfilled with a N2/Ar mixture to have an X-ray absorbancy of418Y.Ji et al./Journal of Catalysis 245(2007)415–42720%in the first ion chamber and 80%in the second ion cham-ber.At the Pt L 3edge (11564eV),the estimated resolution was 2eV .To decrease low-and high-frequency noise as much as possible,an acquisition time of 0.5s for the EXAFS data was used,with a gradual increase to 1.5s at high photon energy,and three scans were averaged.The samples were pressed into self-supporting wafers (cal-culated to have an absorbency of 2.5)and placed in a controlled atmosphere cell operated at 1atm [14].The samples were dried in the cell in flowing He for 60min at 150◦C.The Pt/Y sam-ples were then reduced in flowing hydrogen at 300◦C (heating rate,5◦C /min)for 1h and cooled to room temperature (25◦C)in flowing hydrogen,after which spectra were taken in flow-ing H 2.The samples were then heated in flowing H 2to the next higher temperature (100,200,300,and 400◦C),where again the spectra were taken.After reaching the highest temperature (400◦C)in flowing H 2,the samples were cooled again in flow-ing H 2to room temperature,followed by an evacuation for 1h.XAFS spectra were again obtained in vacuum at room tem-perature and after heating to the next-higher temperature.The former sequence of XAFS data represents the Pt samples with hydrogen chemisorbed at a particular temperature (H/Pt),and the latter sequence of data represents the Pt samples under vac-uum at the same temperature (Pt)with the evacuation treatment at room temperature as the first treatment.2.2.Model for hydrogen chemisorptionThe adsorption of hydrogen can be described with a Frumkin adsorption isotherm [15],by assuming that the Gibbs free en-ergy of hydrogen adsorption is linear with H coverage (θH ).This leads to the following equilibrium constant:(1)K H =θ2H P H 2(1−θH )=e −( G 0H +g H θH )/RT .Here P H 2is the hydrogen gas pressure, G 0H = H −T S is the Gibbs free energy of hydrogen adsorption (per mole of H 2)at zero hydrogen coverage,and g H is the hydrogen–hydrogen lateral interaction constant.Because both H and S can change with coverage,the lateral interaction constants can be written as g H =h −T s ,where h and s are the corre-sponding enthalpy and entropy interaction constants.Thus,the Frumkin adsorption isotherm implies that the hydrogen adsorp-tion bond becomes weaker ( G less negative)with increased hydrogen coverage,as shown schematically on the right side of Fig.1.The weaker adsorption on a surface already covered with adsorbates results from either lateral interactions (directly or through the Pt substrate)or from ligand effects [16]of al-ready adsorbed H,weakening the interaction with additional H.Rearranging Eq.(1)gives the hydrogen coverage (θH )per Pt atom at any temperature (T )and hydrogen gas pressure (P H 2),(2)θH =P 1/2H 2e −1/2( G 0H +g H θ)/RT1+P 1/2H 2e −1/2( G 0H +–gH θ)/RT .This work uses the three-site adsorption model of Oudenhuijzen et al.[4]discussed above,with ontop (ot),n -fold (n f),and atop(at)adsorption sites in the order of increasing Pt–H adsorptionenthalpies,as shown in Fig.1.Within each site,g H =h −T s is set to zero.Equation (2)now can be used to determine the coverage,θi ,at each site,with the total H coverage/Pt atom then given by(3)θH =N at θat +N n f θn f +N ot θot ,where N i is the number of each type of site on the cluster nor-malized per Pt atom.In addition to atomic H on the Pt surface,physisorbed mole-cular H 2will be present on the surface of the catalysts (Pt and support)at the T and P H 2used in the H/M experiments.To de-scribe the physisorption of molecular H 2,a Temkin isotherm [15]is introduced,(4)K H 2=θ2H 2P H 2(1−θH 2)=e−( G 0H 2+αP H 2)/RT.A Temkin isotherm assumes that G increases (decreasesin magnitude)linearly with hydrogen pressure.The Temkin isotherm is now more appropriate because it includes adsorp-tion on many different types of sites,the metal cluster and thesupport.Note that θH 2is proportional to P H 2rather than P 1/2H 2,making θH 2have a totally different dependence on the hydrogen pressure P H 2than θH .The total coverage θ=N H 2θH 2+θH per Pt atom now de-pends on several unknown parameters:N i (i =ot,at,n f,and phys.), H i ,and S i for each site.It is obvious that the num-ber of parameters must be limited to make the model practical.The entropy change for the reaction (5)(1/2)H 2+Pt ∗→H/Pthas been estimated to be 0.085kJ /(kmol H)[17].This is a per-fectly reasonable result because the absolute entropy of H 2(i.e.,H 2→2H)is 0.13kJ /(kmol H 2)[18][or 0.065kJ /(kmol H)],and the adsorbed atomic H on the surface should have relatively much smaller entropy.This value for S is used for all H ad-sorption sites and twice the value 0.170kJ /(kmol H 2)for the H 2physisorption.This then leaves two parameters (N i and θi )for each of the four adsorption sites (three chemisorption sites plus one physisorption site)plus the “Temkin”parameter,α,for a total of nine parameters to reproduce the coverage over a wide range of T and P in the H/M experiments.In fitting the TPD data,the numerical derivatives,d θi /d T ,of the expressions in Eqs.(1)and (3)are used.Only six parameters are necessary,because physisorbed hydrogen does not need to be taken into account;at low pressure,the physisorbed H leaves well below the temperatures used in the TPD experiments.One additional aspect must be built into the model.Gas-phase TPD experiments along with vibrational spectroscopy,as well as in situ Raman probe studies in an electrochemical cell,show the existence of ontop H,as discussed above [3].This ontop H is definitely in an atop position,as indicated by both the Delta XANES signature and vibrational spectroscopy fre-quencies.An important question is:How can this H adsorb in atop sites if these very same atop sites were first filled at very low coverage?This fact indicates that the atop sites at cornersY.Ji et al./Journal of Catalysis245(2007)415–427419 and edges,althoughfilled atfirst,become vacant again with in-creasing coverage.This suggests that with increasing coverage,lateral interactions force H to leave the atop positions.This isexactly consistent with ADF calculations on H n/Pt4clusters re-ported by us recently[4,10],which indicate that indeed the atopsite is occupied for the cluster H/Pt4.However,for two H atomson Pt4,two n-fold(i.e.,either twofold bridged or n-fold fcc)sites are preferred.This is now included in the model by assum-ing that for each H atom adsorbed in the n-fold site,one atop Hmoves over to a n-fold site.Thus the atop sitesfillfirst;thenfill-ing of the n-fold sites begins with a simultaneous emptying ofthe atop sites,followedfinally byfilling of the ontop sites whenthe n-fold sites arefilled.If these atop and ontop sites were ex-actly the same sites,then the condition that N ot=N at mightbe required.However,it also might be assumed that the atop ton-fold site shift occurs only at certain corner or edge sites.ThusN at and N ot are allowed to vary independently.If they were tocome out similar when the H/M data werefitted,then conclu-sions could be drawn as to the exact nature of these ontop sites(see Section4).Although the total coverage with chemisorbed hydrogen,θH,is determined by Eq.(3),the H may be mobile on the surface.Therefore,H does not necessarily stay where it was initiallyadsorbed,but rather may move to the most stable available sites.This mobility can be accounted for simply by moving all Hregardless of where it was initially adsorbed to the atop sitesfirst(having the largest H).This will lead tofilling of then-fold sites while at the same time gradually rearranging theH in atop sites to n-fold sites,as indicated above;eventually,all available ontop sites having the smallest H will befilled.In this simplified model,H mobility does not affect the totalH coverage,but affects only the maximum coverage of eachtype of site,namely N i.Therefore,the N i’s in Eq.(3)do notnecessarily indicate the average total number of each type ofsite available on the clusters,but rather indicate the maximumcoverage of each type of site during the uptake of H2.Thus aN i of0.5means that only about1/2of these types of sitesfillwith H,at which point lateral interactions force the H into thenext site with lower energy.It will be shown below that the N i’s are dependent on eitheruptake or desorption of H2.For instance,in TPD experiments orin the XANES data,the temperature is raised either in vacuumor inflowing H2,leading to desorption of H and thereby empty-ing sites.In contrast,in hydrogen chemisorption experiments,H uptake is observed with increasing pressure at constant tem-perature,beginning with a clean surface.The dependence of N ion uptake/desorption can be attributed to the kinetics of the re-arrangement and produces a hysteresis in the sitefilling process,as discussed more fully below.2.3.Delta XANES techniqueIt is well known even from early work that the Pt L3XANESis sensitive to the adsorption of H[19–22].To isolate and iden-tify these rather small changes,difference spectra μare ob-tained by taking the difference between the L3spectra withand without H, μL3=μL3(H/Pt)−μL3(Pt),withμL3(H/Pt)the L3-edge spectrum in the presence of H2andμL3(Pt)theL3-edge spectrum in vacuum.Because the absorptionμequalsμ0(1+χ),the total change can be expressed as[2]μL3=μL3(H/Pt)−μL3(Pt)(6)= μ0+ (μ0χPt–Pt)+μ0,H/PtχPt–H,where μL3is the L3-edge difference spectrum,μL3(H/Pt)is the L3-edge spectrum in the presence of H2,μL3(Pt)isthe L3-edge spectrum in vacuum, μ0represents changesin the atomic L3XAFS with H coverage, (μ0χPt–Pt)rep-resents changes in the Pt–Pt total scattering induced by H2chemisorption,μ0,H/Pt is free-atom L3absorption(includingatomic XAFS)in the presence of H2,andχPt–H represents ad-ditional Pt–H scattering.The FEFF8code[5]was designed to calculateμjust as ob-tained in experiments.FEFF8performs real-space full multiplescattering calculations using a muffin-tin potential calculatedwith a Hedin–Lundquist exchange correlation approximationand implements self-consistentfield potentials for the deter-mination of the Fermi level and the charge transfer.Thus μcan be calculated by performing the same μdifference as ob-tained experimentally.Fig.2shows the total μ[minus thefirstterm in Eq.(6)]obtained from FEFF8calculations on Pt6clus-ters.As in previous work[23],the μ0contribution was notincluded in Fig.2because it should be relatively small.More-over,the μ0contribution is exaggerated for these very smallclusters modeled here by the FEFF8calculations.These FEFF8results show the importance of changes in thePt L3XANES region due to the influence of chemisorbed Hon the Pt–Pt multiple scattering paths.When H atoms are ad-sorbed on the n-fold hollow sites,hydrogen weakens the Pt–Ptbonding for Pt atoms beneath the H adsorption site[the secondterm on the right in Eq.(6)].This bond weakening has beencalled d-electron frustration by Feibelman and Hamann[24],and Pt–Pt destabilization by Papoian et al.[25].The theoreti-cally obtainedfingerprints for atop and n-fold H,as shown inFig.2,have been experimentally confirmed by Teliska et al.[3]and Oudenhuijzen et al.[4].The experimental XANES data have to be carefully alignedbefore taking the differences as indicated in Eq.(6).Thisalign-Fig.2.Previously reported μtheoretical signatures obtained from FEFF8cal-culations on the clusters indicated for atop,2-fold bridged,and n-fold fcc H.420Y.Ji et al./Journal of Catalysis 245(2007)415–427ment procedure has been carefully outlined previously [22].First,the zero of energy is set to the energy that falls at 0.6in both the normalized μL 2(H/Pt )and μL 2(Pt )spectra.Then the EXAFS features in each of the μL 2and corresponding μL 3spectra are aligned using a computer routine that minimizes the square of the difference μL 3−μL 2in an energy range usu-ally between 30and 100eV above the edge.This energy range has been varied some in our previous work,depending on the data [4].This entire energy alignment procedure,used in all of our previous gas-phase work,is critical to obtaining systematic μspectra because of the large cancellations involved in the differences,leaving μL 3typically only around 0.03–0.06in magnitude.3.Results 3.1.TPDThe TPD data collected on the Pt/H-LTL and Pt-K-LTL cat-alysts are displayed in Figs.3a and 3b (dashed dotted lines).A weak asymmetry at low T can be observed for Pt/H-LTL (Fig.3a).The TPD of Pt/K-LTL has shoulders at around 300and 500K (Fig.3b).The TPD data were fitted with a six-parameter fit using Eqs.(2)and (3).The total fits are indicated in Figs.3a and 3b with solid lines.It can be seen that the three-site model adequately describes the TPD data.The individual components are also plotted in Figs.3a and 3b .The negative contribution in the atop component is due to therearrangementFig.3.TPD data collected on (a)Pt/H-LTL and (b)Pt/K-LTL (-·-·).Fit with three site adsorption model (6parameters)(—).The components include the ontop (ot,···),n -fold (n f,---),and atop (at,–––).Table 1Summary of TPD fit parameters using derivative of Eq.(3)and 3-site model for the LTL samplesPt/H-LTL Pt/LTL N sitesH (kJ /mol)N sites H (kJ /mol)Atop 0.32±0.05−49±20.35±0.05−71±2n -fold0.52±0.05−43±20.51±0.05−46±2Ontop (weak)Not observed0.26±0.05−32±2from n -fold sites to atop sites and will be further explained in Section 4.The number of filled sites per Pt surface atom and the adsorption enthalpy of each type of site are given in Table 1.It can be seen that the number of filled atop sites is lower than the number of filled n -fold sites for both Pt/LTL catalysts.Ta-ble 1also shows that the H i values for the basic Pt/K-LTL catalyst are more negative,pointing to a stronger Pt–H bond for each type of chemisorption site on Pt particles dispersed in a basic zeolite.The Pt–H bond strength is increasing in the order ontop <n -fold <atop for each catalyst.Obviously,the Pt–H bond strength for the ontop site is so low for the acidic Pt/H-LTL that no hydrogen is chemisorbed on these sites in vacuum,but these sites serve as catalytic sites to dissociate H 2,which then spills over to the support.The spillover peak arising from desorption of H from the support is present in the TPD data at high temperature and is indeed very intense for the Pt/H-LTL catalysts.These same ontop sites in the K-LTL sample also probably produce spillover,but to a lesser extent.3.2.H/M chemisorptionFig.4shows the first isotherms for Pt/H-USY and Pt/NaY and the least squares fits for each using the adsorption model described above for the six different temperatures of adsorp-tion.The corresponding parameters obtained from these fits are given in Table 2.The separate components for H chemisorp-tion and H 2physisorption and the separate atop,threefold,and ontop components of the H chemisorption for each adsorption temperature and support calculated from the fits are plotted in Figs.1and 2in supplementary material.The agreement between the fits and experiment is reason-able,considering that 150points are fit with 9parameters.No matter where the iterative nonlinear least squares process was started,the final result was the same,indicating these fits cor-respond to the true minimum.The Temkin isotherm for the physisorbed H 2was clearly required to give a reasonable fit.As expected,for physisorption,a very small H phys and a very large N phys was found for each support.H 2can physisorb not only on the Pt particles,but also on the zeolite.The Temkin isotherm shows that the value of H phys increased from about −4to nearly 0kJ /mol (an effective decrease of H phys )with increasing adsorption temperature,also consistent with its prop-erties.The fits in general show a curvature that is too small at low pressure.This clearly suggests that the H for each site may be larger initially and then decrease with coverage (i.e.,a Frumkin isotherm for each site).A Frumkin isotherm for each site would introduce at least three additional parameters (h i for each site),。

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