有机膨润土的吸附性能研究

有机膨润土处理水中有机物的研究已有报道［1－4］，但尚无就改性所用的表面活性剂对有机膨润土吸附性能的影响及规律的系统研究，对有机膨润土与不同有机物间作用机理的报道也甚少［1］．本文用3种不同的阳离子表面活性剂改性膨润土，并从等温吸附线的特征和有机物的辛醇－水分配系数较系统地研究了有机膨润上对几种有机物的吸附性能和作用机理．1实验部分1．1材料原士为钠基膨润土，经测定其阳离子交换容量为7464meg／100g土；澳化十六烷基王甲铰（CTMAB）为分析纯，溪化十二烷基三甲铰（DTMAB，95％），演化十八烷基三甲按（OTMAB…     

表面活性剂改性的螯合剂有机膨润土对水中有机污染物和重金属的协同吸附研究

采用季铵盐阳离子(CTMA+)和有机螯合剂(Am)复合改性膨润土(IMB), 制得一系列螯合剂柱撑膨润土IMB-CTMA-Am. 利用X射线衍射(XRD)分析、差热-热重(TG-DTA)分析、比表面积测定(N2-BET)以及元素分析等手段对吸附剂样品进行了表征. 结果表明, CTMA+和Am已柱撑进入膨润土层间. 吸附实验结果表明, IMB-CTMA-Am能同时有效地去除有机污染物对硝基苯酚(PNP)和重金属铅(Pb2+), 其对水中对硝基苯酚的强吸附能力来源于分配作用的增加和层间距的增大, 而与比表面积无关. 傅里叶变换红外光谱(FTIR)显示, IMB-CTMA-Am吸附Pb2+后的N—H吸收峰向低频方向移动, 表明Pb2+和膨润土层间的Am形成了稳定的配合物. 有机螯合剂Am和Pb2+所形成配合物的稳定性越大, IMB-CTMA-Am对Pb2+离子的吸附能力也就越强.     

双阳离子复合改性膨润土的吸附性能与构效关系

膨润土是一种以蒙脱石为主要成分的天然吸附材料. 本文用2-巯基乙胺盐酸盐(MEA)与十六烷基三甲基溴化铵(HDTMA)复合改性内蒙钙基膨润土(IMB), 制得具有特殊结构与性能的吸附材料MEA-HDTMA-IMB. X射线衍射(XRD)、红外光谱(FT-IR)、热分析(TG-DTA)及比表面积(N2-BET)等结构表征表明: 复合改性膨润土的比表面积和层间距显著增大. 吸附研究发现: MEA-HDTMA-IMB能同时有效吸附混合水溶液中的有机物对硝基苯酚和重金属铜. 复合改性膨润土对水中有机物的吸附机理以分配作用为主, 其吸附能力强于用季铵盐阳离子单一改性的有机膨润土HDTMA-IMB; 对水中重金属的吸附主要为络合反应, 其吸附性能与用巯基铵阳离子单一改性的膨润土MEA-IMB相当.     

改性粘土吸附去除水中有机毒物的研究进展

改性粘土吸附去除水中有机毒物的研究进展向阳，刘军（同济大学环境工程学院，上海２０００９２）前言在水体的有机毒物控制技术中，活性炭吸附法被广泛应用。但其存在着价格较贵，再生困难（高温高压）等缺点，于是人们开始尝试采用价格低廉的天然吸附材料来取代活性炭，...     

DHAC改性膨润土对炼油碱渣废液的吸附机理探讨

以有机插层剂双十八烷基二甲基氯化铵(DHAC),对新疆夏子街膨润土进行插层改性,制备DHAC改性膨润土。红外光谱(FTIR)分析表明,双烷基阳离子插层进入蒙脱石片层。X射线衍射(XRD)表明,DHAC改性膨润土片层间距为3．772 nm,为改性前的2．07倍,表明改性后蒙脱土片层间距增大。SEM分析观察, DHAC捕层改性后膨润土颗粒更加疏松,蒙脱石颗粒表面有明显的刻蚀痕迹。通过研究改性膨润土的吸附机理分析表明,DHAC改性膨润土在不同温度下的等温吸附模型符合Freundlich模型,且相关性较高。挥发酚在改性膨润土上的吸附焓值为-2．64 kJ／mol,属于物理吸附,且△Gθ<0,说明该吸附为自发的放热过程。室温下DHAC改性膨润土吸附挥发酚的动力学模型遵循Bingham和Langmuir速率方程。     

有机膨润土吸附水中重金属和有机污染物的性能及机理研究

螯合剂柱撑有机膨润土IMB-TMA-Am能有效吸附水中有机物对硝基苯酚(PNP)和重金属离子Cu2 ,其中IMB为内蒙膨润土;CTMA为溴化十六烷基三甲基季铵盐阳离子;Am分别为有机螯合剂乙二胺(En)、三乙烯四胺(TETA)和四乙烯五胺(TEPA)。实验结果表明:螯合剂柱撑有机膨润土对有机污染物的吸附主要表现为有机物在长碳链疏水介质中的分配,其吸附能力和膨润土内有机碳、氮含量一致;对水中重金属离子的吸附机理是Cu2 和进入膨润土层间的有机螫合剂Am形成了配合物,其吸附能力和所形成配合物的稳定性一致。     

活性炭的表面化学改性及其对有机硫化物的吸附性能的研究

活性炭; 表面化学改性; 有机硫化物; 吸附性     

有机改性凹凸棒土对腐殖酸的吸附性能研究

合成了十六烷基三甲基氯化铵(CTAC)改性的凹凸棒土吸附剂,并研究了其对水中腐殖酸的吸附行为。通过FTIR、TG对改性前后凹凸棒土进行表征。结果表明,十六烷基三甲基氯化铵成功结合到凹凸棒土表面,结合到凹凸棒土表面的量为9.78%。在25℃时,腐殖酸在吸附剂上吸附行为符合Freundlich方程,吸附动力学符合拟二级动力学方程,初始浓度为54.60~200.20mg/L时,ATP-CTAC对腐殖酸的最大吸附量为253mg/g;温度对吸附行为影响不大;改性后的凹凸棒土对腐殖酸的吸附随pH的增大而降低;改性后的凹凸棒土显著地提高了对腐殖酸的吸附量。     

十六烷基三甲基溴化铵改性膨润土对直接黑染料的吸附及机理

用十六烷基三甲基溴化铵改性膨润土(有机膨润土),用红外光谱和固体紫外漫反射光谱等对有机膨润土的结构进行了分析。研究了有机膨润土对水中直接黑染料的吸附和机理。用0.05g有机膨润土处理浓度为70mg/L的直接黑溶液时(303K),脱色率达到72.6%,平衡吸附量为20.5mg/g,有机膨润土对直接黑染料的吸附符合Freundlich吸附等温方程,从热力学结果来看,是化学吸附和物理吸附共同作用的过程。     

有机膨润土对水中苯、甲苯、乙苯、二甲苯和铬酸根离子的吸附性能

污水处理;有机膨润土对水中苯、甲苯、乙苯、二甲苯和铬酸根离子的吸附性能     

Electrospinning of polyurethane/organically modified montmorillonite nanocomposites

Polyurethane/organically modified montmorillonite (PU/O‐MMT) nanocomposites were electrospun and the effect of O‐MMT on the morphology and physical properties of the PU/O‐MMT nanofiber mats were investigated for the first time. The average diameters of the PU/O‐MMT nanofibers were ranged from 150 to 410 nm. The conductivities of the PU/O‐MMT solutions were linearly increased with increasing the content of O‐MMT, which caused a decrease in the average diameters of the PU/O‐MMT nanofibers. The as‐electrospun PU and PU/O‐MMT nanofibers were not microphase separated. The exfoliated MMT layers were well distributed within the PU/O‐MMT nanofibers and oriented along the fiber axis. When the PU/O‐MMT nanofibers were annealed, the exfoliated MMT layers hindered the microphase separation of the PU. The electrospinning of PU/O‐MMT nanocomposites resulted in PU nanofiber mats with improved Young's modulus and tensile strength. © 2005 Wiley Periodicals, Inc. J Polym Sci Part B: Polym Phys 43: 3171–3177, 2005     

溴化铵改性膨润土脱除气态单质汞的特性及机理分析

采用溴化铵对钠基膨润土进行改性制得脱汞吸附剂,在固定床实验装置上对所制备的吸附剂进行脱汞性能测试。脱汞实验结果表明,钠基膨润土较钙基膨润土在脱汞性能上提高不大,而溴化铵改性的钠基膨润土(Br-Ben/Na)脱汞性能得到明显提高,脱汞效率达到97.7%。吸附温度的升高有利于对Hg0的脱除,在140℃下,10%Br-Ben/Na吸附剂的脱汞率能长时间保持在90%以上,说明在此吸附过程中化学吸附占主导性作用。通过N2吸附/脱附、X射线衍射(XRD)、元素分析仪和傅里叶变换红外光谱(FT-IR)分析等结果表明,改性后的膨润土比表面积下降,平均孔径增大;铵根离子进入到膨润土的层间置换出层间钠离子,煅烧活化过程中层间的铵根离子并未分解,而在层间与膨润土结合为某吸附活性组分协助Br-与Hg0反应,提高了膨润土的脱汞性能。     

卟啉钒在改性高岭土上的吸附行为及机理研究

利用酸改性和负载钼的酸改性高岭土作为吸附剂研究了环己烷中的卟啉钒(钒氧-2,3,7,8,12,13,17,18-八乙基卟啉,VO-OEP)在这两种吸附剂上的吸附行为,从热力学角度探讨了吸附机理。结果表明,两种吸附剂对卟啉钒的吸附符合Langmuir吸附等温线,卟啉钒单层吸附在改性高岭土上;吸附表现为自发热过程,吸附热均大于40 kJ/mol,说明吸附形成了化学键。     

DC electrorheological response of polyethylene/organically modified layered silicate nanocomposites

The present work reports the electrorheological (ER) response of high‐density polyethylene (HDPE)/organically modified silicate layers nanocomposites based on four commercially available HDPE matrices. Two single‐site catalyzed bimodal resins, one single‐site catalyzed unimodal resin and one Ziegler–Natta catalyzed unimodal resin are studied. It is revealed that the distinct separation of the two modes of the bimodal HDPE resins significantly enhances the ER response. It is proposed that the slower structural relaxation modes introduced by higher molecular weight species in the bimodal HDPE matrices enhance the ER response of the nanocomposites. This is ascribed to the longer induction time for leaking current density, which is an indicator of mobility and release of immobilized cationic surfactants at the silicate layers surface induced by field exposure. It is found that the screening effect of prematurely released cationic surfactants leads to a weaker ER response in nanocomposites whose matrices have faster relaxation modes. © 2017 Wiley Periodicals, Inc. J. Polym. Sci., Part B: Polym. Phys. 2017 , 55, 1298–1309     

有机修饰氧化硅对抗紫外纳米ZnO的原位表面修饰

以正硅酸乙酯和二甲基二乙氧基硅烷作为共前驱体,通过溶胶-凝胶反应得到有机修饰氧化硅;用有机修饰氧化硅对碱式碳酸锌进行原位表面改性,通过对表面改性碱式碳酸锌进行热处理得到表面改性纳米ZnO;分析了表面改性纳米ZnO的结构和性能.结果表明,经有机修饰氧化硅改性处理的纳米ZnO具有强憎水性,与有机相的相容性较强,光催化活性得...     

Dynamic mechanical analyses of Nafion®/organically modified silicate nanocomposites

Nafion®/organically modified silicate (ORMOSIL) hybrids were generated via polymer in situ sol–gel copolymerizations of tetraethylorthosilicate (TEOS) with difunctional and trifunctional organoalkoxysilane monomers, and the dynamic mechanical relaxations and thermomechanical stability of the resultant composites were investigated. All ORMOSIL fillers restrict main‐chain and side‐chain mobility. The results suggest that sulfonic acid side chains become entrapped in silicate or ORMOSIL structures that evolve during the in situ sol–gel process. Some but not all of the ORMOSIL combinations display trends in the α or β relaxation temperature with respect to the TEOS comonomer ratio. All of the hybrids have greater high‐temperature thermomechanical stability than the unfilled acid form. There are definite composition trends in the vertical displacement of the storage‐modulus–temperature curves. For some of the semiorganic comonomers, there is a monotonic increase in storage modulus with decreasing comonomer content in the high‐temperature regime, which is understood in terms of a progressive immobilization of the long side chains by progressively more rigid ORMOSIL nanostructures. For other semiorganic comonomers, the high‐temperature plateau shifts upward to a maximum and then shifts downward with decreasing comonomer fraction. In addition to the chemical nature of the imparted nanophases, these molecular motions are expected to influence the transport properties of these novel heterogeneous membranes. © 2001 John Wiley & Sons, Inc. J Polym Sci Part B: Polym Phys 39: 1282–1295, 2001     

Adsorption behavior of end-functionalized polymers modified by iminium ion

In order to clarify the end-functionalization effect of polymers modified by iminium ion, a model compound with a modified chain end was prepared by directly reactingn-butyllithium withN-methyl-2-pyrrolidone and then quenching by the addition of methanol. It is shown that the model compound includes the iminium ion group and that the adsorption bands in the IR-spectra of the chemically modified polymer were similar to those of model compoundThe adsorption behavior of end-functionalized polystyrene(PS-X) and diblock copolymer of PS and polybutadiene(PB) which were modified by iminium ion(PS-PB-X), were examined over a wide range of molecular weights of these polymers. It is evident that the amount of adsorption increased significantly by the end-functionalization and this trend was especially strong in the low molecular weight polymers (M _w<-10⁵). The preference for the end-functionalized polymer was also examined by competitive and sequential adsorption experiments between different molecular weight species. It is shown that a prefered adsorption of PS-X with low molecular mass is pronouced over the adsorption of PS or PS-X with high molecular weight and in the combination of high and low molecular weight species of PS-X, a special enhancement of total adsorption can be observed. This enhancement is based on a combination of different adsorption layers formed by these two molecular weight species.     

Adsorption of organochlorine pesticides on modified porous Al30/bentonite: Kinetic and thermodynamic studies

Adsorption of pesticides (heptachlor epoxide, dieldrin and endrin) onto modified bentonite by Keggin cation [Al₃₀O₈(OH)₅₆(H₂O)₂₄]¹⁸⁺ denoted Al₃₀ cation to form composite (Al₃₀/B), has been investigated as a possible alternative method for their removal from aqueous solutions. The study was aimed to use a low-cost material as a step towards cleaner environment. Interestingly, these chemical modifications altered the physicochemical characteristics of bentonite in term of morphology, surface area and functionality which has been confirmed by using nitrogen adsorption–desorption isotherm, scanning electronic microscopy (SEM) and X-ray diffraction (XRD). Gas chromatography coupled to mass spectrometry (GC–MS) was used to identify and analyze the pesticides. Different physicochemical parameters were analyzed: contact time, adsorbent dose, pH, and temperature. The results showed that the removal percentage of pesticides on Al₃₀/B was the highest at contact time of 5 h, adsorbent dosage of 25 mg, at pH 7.5, and at optimum temperature of 45 °C. Furthermore, the Kinetic study indicated that the adsorption of pesticides on Al₃₀/B was well adapted to the pseudo-first order kinetic with a correlation coefficient near unity. The results of adsorption were fitted to the Langmuir and Freundlich isotherms. The Freundlich model represented the adsorption process better than Langmuir model, with correlation coefficients (R²) values range from 0.986 to 0.989. The Thermodynamic study suggested that the adsorption of pesticides was chemisorption, spontaneous and endothermic process. Therefore, Al₃₀/B composite can be utilized effectively for removal of pesticides with efficiency up to 98%.     

Thermal behavior of a bentonite

The mineralogical composition of the Kütahya calcium bentonite (CaB) from Turkey was obtained as mass% of 60% calcium rich smectite (CaS), 30% opal-CT (OCT), trace amount illite (I), and some non-clay impurities by using chemical analysis (CA), X-ray diffraction (XRD), and thermal analysis (TG-DTA) data. The crystallinity, porosity, and surface area of the samples heated between 25–1300°C for 2 h were examined by using XRD, TG, DTA and N₂-adsorption-desorption data. The position of the 001 reflection which is the most characteristic for CaS does not affect from heating between 25–600°C and then disappeared. The decrease in relative intensity (I/I ₀) from 1.0 to zero and the increase in full width at half-maximum peak height (FWHM) from 0.25 to 1.0° of the 001 reflection show that the crystallinity of the CaS decreased continuously by rising the heating temperature from 25 to 900°C and then collapsed. The most characteristic 101 reflection for opals intensifies greatly between 900 and 1100°C with the opal becoming more crystalline. The total water content of the natural bentonite after dried at 25, 105 and 150°C for 48 h were determined as 8.8, 5.0 and 2.5%, respectively. The mass loss occurs between 25 and 400°C over two steps with the maximum rate at 80 and 150°C, respectively. The exact distinction of the dehydration temperatures for the adsorbed water and interlayer water is seen almost impossible. The temperature interval, maximum rate temperature, and mass loss during dehydroxylation are 400–800°C, 670°C and 4.6–5.0%, respectively. The maximum rate temperatures for decrystallization and recrystallization are 980 and 1030°C, respectively. The changes in specific micropore volume (V _mi), specific mesopore volume (V _me), specific surface area (S) were discussed according to the dehydration and dehydroxylation of the CaS. The V _mi, V _me and S reach to their maxima at around 400°C with the values of 0.045, 0.115 cm³ g⁻¹ and 90 m² g⁻¹, respectively. The radii of mesopores for the bentonite heated at 400°C are distributed between 1–10 nm and intensified approximately at 1.5 nm.