壳聚糖吸附Cd2+的机理

壳聚糖分子中的大量氨基及部分酰胺基的存在 ,能够选择性地配位或吸附一些金属离子 ,尤其是对过渡金属离子具有较好的螯合能力。Ｐｉｒｏｎ等[2 ] 利用放射性85Ｓｒ研究了壳聚糖的氨基与碳酸锶离子对Ｓｒ2 +、ＣＯ2 -3 之间形成的三元络合物的结构。季君晖[3] 通过光电子能谱研究发现 :壳聚糖螯合Ｃｕ2 +,只与壳聚糖中的—ＮＨ2 配位。Ｔｓｅｚｏｓ[4] 利用ＩＲ、ＭＳ和ＥＰＲ说明铀与壳聚糖的络合点为氨基的氮原子。Ｇｕｉｂａｌ等[5] 用ＩＲ、ＣＰ ＭＡＳ1 3ＣＮＭＲ及反射光谱法证实吸附机理涉及氨基。含镉废水是危害较大的工业废水之一 …     

交联壳聚糖树脂吸附Cu2+的机理研究

研究了甲醛、环氧氯丙烷交联壳聚糖(AECTS)对Cu2+的吸附热力学行为,用FTIR对吸附产物进行了结构表征,并研究了溶液中介质种类的不同对Cu2+吸附量的影响.结果表明AECTS主要以配位形式吸附Cu2+;AECTS对Cu2+的吸附符合Langmuir等温方程,属于单分子层吸附;吸附为自发的、吸热的熵增加过程;同时不同介质对树脂吸附Cu2+的影响大小顺序为HCl＞CdCl2＞MgCl2＞NaCl,并对其作用机理进行了探讨.     

交联壳聚糖对Zn2+的吸附性能

研究了甲醛、环氧氯丙烷交联壳聚糖树脂(AECTS)对Zn 2 的吸附行为,探讨温度、溶液的pH、反应时间、再生次数等因素对吸附性能的影响,并用红外光谱(FTIR)和光电子能谱(XPS)对吸附产物表面的元素结构及其结合能的变化进行表征. 结果表明,AECTS对Zn 2 的吸附导致AECTS结构和性能发生显著变化. FTIR和XPS分析表明,Zn 2 以配位键的形式吸附于AECTS,使AECTS中氨基的伸缩振动、变形振动发生了明显变化,N原子发生化学位移,而AECTS分子链上的羟基没有直接参与配位反应;AECTS对Zn 2 有较强的吸附能力和较快的吸附速率,在30 ℃、Zn 2 初始质量浓度为1 g/L的溶液中,吸附量可达163 mg/g树脂,是壳聚糖饱和吸附量的1.7倍左右;吸附量受pH的影响较大,在pH＝5时吸附量最高;AECTS对Zn 2 的吸附行为符合Freundlich等温吸附方程,温度升高吸附量增大,该过程为一吸热过程;AECTS经再生重复使用5次,吸附量基本不变.     

壳聚糖对Zn2+的吸附性能研究

本文用壳聚糖对Ｚｎ＾２＋的吸附条件进行了研究,探讨了脱乙酰度,分子量,粒度大小,溶液的ｐＨ值,温度,Ｚｎ＾２＋起始浓度和不同锌盐等方面对壳聚糖吸附性能的影响。结果表明：壳聚糖对Ｚｎ＾２＋的吸附具有Ｌａｎｇｍｕｉｒ吸附特征,其吸附最佳条件是壳聚糖脱乙酰度为１００％,锌盐为硫酸锌,Ｚｎ＾２＋溶液ｐＨ值为６．０,起始浓度４－５ｍｇ／ｍｌ。     

壳聚糖黄原酸盐对Cu2+的吸附性能

用红外、紫外和热重分析等测试技术分别对二硫代氨基甲酸改性壳聚糖(壳聚糖黄原酸钠,DTC-CTS)进行了表征和测试.比较了DTC-CTS与未改性的壳聚糖(CTS)对水溶液中Cu2 吸附性能的差别,考察了溶液的pH值、温度、时间及取代度对其吸附性能的影响.结果表明,DTC-CTS的取代度越高,吸附性能越好,对Cu2 吸附的最佳pH值范围为6.0～7.0,最佳温度为40℃,最佳吸附时间为0.5h.在最佳吸附条件下,DTC-CTS的吸附量为349.5mg/g,比CTS提高了7%.用体积分数为10%的氨水可将吸附在DTC-CTS上的Cu2 定量的洗脱,脱附率为96%,DTC-CTS能重复使用3次.     

改性磁性壳聚糖微球对Cu2+、Cd2+和Ni2+的吸附性能

Fe3O4/ chitosan magnetic microspheres of 50 to 80 滋m were prepared using the inverse phase emulsion dispersion and chemical crosslinking technology, and then modified with ethylenediamine for use in the adsorption of heavy metal ions. The adsorption properties of the modified Fe3O4/chitosan toward Cu2+, Cd2+ and Ni2+ were investigated. It was found that the adsorption capacities of Cu2+ and Ni2+ increased with pH, and a maximum adsorption for Cd2+ occurred at pH=3. The saturated adsorption capacities calculated by Langmuir isotherms were 54.3 mg·g-1 for Cu2+, 20.4 mg·g-1 for Cd2+, and 12.4 mg·g-1 for Ni2+, respectively. The adsorption kinetics were well described by pseudo-second-order equation models. The experimental results showed that the Fe3O4/chitosan modified with ethylenediamine presented higher adsorption selectivity for Cu2+ than for Cd2+ and Ni2+ in all studied pH ranges.     

Cu2+-壳聚糖螯合物及壳聚糖吸附Cu2+机理的XPS研究

吸附机理;XPS;Cu2+-壳聚糖螯合物及壳聚糖吸附Cu2+机理的XPS研究     

交联壳聚糖树脂吸附Co2+的机理研究

研究了甲醛、环氧氯丙烷交联壳聚糖 (AECTS) 对Co2 的吸附热力学行为,用FTIR、WXRD对吸附产物进行了结构表征,并研究了溶液中介质种类的不同对Co2 吸附量的影响.结果表明:AECTS主要以配位吸附和物理吸附形式吸附Co2 ;树脂与Co2 配位后,结晶度下降;AECTS对Co2 的吸附行为同时符合Freundlich模型和Langmuir模型;吸附为自发的、放热的熵减小过程;不同介质对树脂吸附Co2 的影响大小顺序为HCl>CdCl2>MgCl2>NaCl,前两者使吸附量减小,后两者使吸附量增加,作用机理相差较大.     

均苯四甲酸酐修饰壳聚糖微球对Pb2+和Cd2+的吸附

用交联的壳聚糖微球(CTS)与均苯四甲酸酐在无水条件下反应,合成了均苯四甲酸酐修饰壳聚糖微球. 用FT-IR和XPS表征了产物的结构,考察了它对水溶液中Pb2+和Cd2+的吸附行为及其影响因素. 结果表明,吸附等温线符合Langmuir方程. 当pH=5.0时,对Pb2+和Cd2+的最大吸附量分别为296.7和149.9 mg/g. 用二级吸附动力学模拟动力学过程有很好的线性相关性,据此确定为化学吸附过程. 以0.2 mol/L的EDTA为解吸剂,Pb2+和Cd2+的再生率分别为92.4%和85.3%.     

交联壳聚糖对氨基酸的吸附性能

本文研究了交联壳聚糖对甘氨酸、谷氨酸和赖氨酸的吸附性能，吸附率依次为甘氨酸＞赖氨酸＞谷氨酸，并决定于上柱液的ＰＨ值及其浓度。用０．０５和０．１ｍｏｌ／ｌＮＨ４ＯＨ可以解吸。     

Adsorption of Cd(II) by Sol-Gel Silica Doped with N-(dipropylcarbamothioyl)thiophene-2-carboxamide

Sol-gel silica was doped with N,N-(dipropylcarbamothioyl) thiophene-2-carboxamide to investigate the sorption of cadmium (Cd) ions from aqueous media. In doped sol-gel silica, the large reagent molecules entrap into pores, whereas, small metal ions diffuse into pores where they make complex with doped reagent. This complexation can be accomplished by either ion exchange or chelation. Doped sol-gel sorbent was applied for removal of Cd(II) from aqueous solution in our study. Adsorption kinetics, adsorption isotherm, equilibration time, effect of initial concentration of adsorbate, and pH effect on the metal removal were studied to optimize the conditions. The prepared adsorbent shows rapid equilibrium and high stability toward high temperature and applied medium. In addition, desorption of metal ions was carried out by 1 M HCl and, thereafter, sol-gel silica adsorbent was regenerated and reused periodically.     

Chemical modification of rose leaf with polypyrrole for the removal of Pb (II) and Cd (II) from aqueous solution

The rose leaf was successfully modified through coating with polypyrrole (PPy) in chemical oxidative route in order to remove Pb(II) and Cd(II) from aqueous media. The rose leaf/polypyrrole (RL/PPy) composites were characterized in terms of morphology, chemical structure, and conductivity properties. The spectrum were obtained from FTIR results which support the formation of RL/PPy composites. FTIR and SEM results indicate that the polypyrrole is completely covered on rose leaf. The conductivity of composite (1.8215 S/cm) was higher than polypyrrole (2.06 × 10^?3 S/cm). The metal removal studies were monitored by Ultraviolet Visible Absorption Spectrometer (UV-Vis). The optimum conditions were detected for adsorption by changing some experimental conditions (such as adsorbent dosage, contact time and stirring speed, initial concentration of the metal solutions and pH). Following the determination of the optimum conditions, the results of the metal removal from wastewater studies were performed by Inductively Coupled Plasma Optical Emission Spectrometry (ICP-OES). Under the optimum conditions, the ICP-OES results obtained for waste water showed the useability of composite for the removal of Pb(II) and Cd(II). The Langmuir and Freundlich models are subjected to adsorption datas. The datas fitted better when by using Freundlich model.     

Preparation and characterization of magnetic bioadsorbent for adsorption of Cd(II) ions

A facile magnetic chitosan composite used for heavy metal ions removal was prepared. The adsorbents with large specific area and rich carboxyl groups exhibited good removal of Cd(II) ions and could be easily separated with magnetic separation. The adsorption capacity of Cd(II) was 48 ​mg ​g⁻¹ and the removal efficiency reached 86.7% after five cycles. Thus, the prepared magnetic chitosan composite could act as a potential adsorbent for Cd(II) ions removal.     

Magnetic Fe3O4/ZIF-8 optimization by Box-Behnken design and its Cd(II)-adsorption properties and mechanism

In this study, the preparation of magnetic Fe₃O₄/ZIF-8 (MFZ) and its adsorption properties for Cd(II) from water were investigated. Various characterizations demonstrate that the as-prepared MFZ has well magnetic-separation performance and thermal stability. In batch adsorption tests, the effects of pH, initial concentration, and adsorbent dosage were evaluated. According to the findings, when the pH is 7 and the dosage is 150 mg/L, the adsorption capacity for a 40 mg/L Cd(II) solution reaches 102.3 mg/g in 180 min. The Cd(II) adsorption processes was found to correspond to pseudo-first-order kinetics and Langmuir model according to the adsorption kinetics and isotherms. The Langmuir model predicted a maximal saturation adsorption capacity of 160.26 mg/g at 298 K. Thermodynamic analysis revealed that the Cd(II) adsorption is an endothermic, spontaneous process. Ion exchange, coordination reaction, and electrostatic interaction are all involved in Cd(II) adsorption by MFZ. The optimum conditions for Cd(II) adsorption were proposed and confirmed in accordance with the results of the response surface optimization experiments. Furthermore, regeneration tests demonstrate the great repeated regeneration ability of MFZ. According to the anticipated production cost, treating wastewater with a Cd(II) concentration of 40 mg/L would cost roughly US$ 8.35/m³. MFZ showed good potential for Cd(II) removal from water.     

Monitoring of Zn(II) and Cd(II) adsorption on activated carbon from aqueous multicomponent solutions by differential pulse polarography (DPP)

The adsorption process of Zn(II) and Cd(II) from aqueous solution has been investigated from both kinetic and equilibrium standpoints, using differential pulse polarography (DPP) on a mercury dropping electrode as the analytical technique. With such an aim, adsorption experiments were performed using not only a single metal ion–Zn(II) or Cd(II) solution but also a multi-component ion metal–Zn(II), Cd(II) and Hg(II) solution. The influence of the pH change in the multi-component ion metal solution on the adsorption of Zn(II) and Cd(II) was also studied. The adsorption processes is relatively fast for Zn(II) and Cd(II). The presence of two foreign ions in the solution slightly speeds up the adsorption process for Zn(II) and significantly slows it down for Cd(II). The adsorption isotherms are similarly shaped for Zn(II) and Cd(II). The addition of the foreign ions has a more unfavourable effect on the adsorption for Cd(II) than for Zn(II). At pH 2, neither Zn(II) nor Cd(II) is adsorbed practically on the carbon. The voltammetric approach has proved to be a fast and efficient method that, at the same time, enables one to monitor the adsorption of Zn(II) and Cd(II) with potential on-line application, which could be useful in waste-water treatment.     

Tuning Photophysical Properties by p-Functional Groups in Zn(II) and Cd(II) Complexes with Piperonylic Acid

Aggregation between discrete molecules is an essential factor to prevent aggregation-caused quenching (ACQ). Indeed, functional groups capable of generating strong hydrogen bonds are likely to assemble and cause ACQ and photoinduced electron transfer processes. Thus, it is possible to compare absorption and emission properties by incorporating two ligands with a different bias toward intra- and intermolecular interactions that can induce a specific structural arrangement. In parallel, the π electron-donor or electron-withdrawing character of the functional groups could modify the Highest Ocuppied Molecular Orbital (HOMO)–Lowest Unocuppied Molecular Orbital (LUMO) energy gap. Reactions of M(OAc)₂·2H₂O (M = Zn(II) and Cd(II); OAc = acetate) with 1,3-benzodioxole-5-carboxylic acid (Piperonylic acid, HPip) and 4-acetylpyridine (4-Acpy) or isonicotinamide (Isn) resulted in the formation of four complexes. The elucidation of their crystal structure showed the formation of one paddle-wheel [Zn(μ-Pip)₂(4-Acpy)]₂ (1); a mixture of one dimer and two monomers [Zn(µ-Pip)(Pip)(Isn)₂]₂·2[Zn(Pip)₂(HPip)(Isn)]·2MeOH (2); and two dimers [Cd(μ-Pip)(Pip)(4-Acpy)₂]₂ (3) and [Cd(μ-Pip)(Pip)(Isn)₂]₂·MeOH (4). They exhibit bridged (1, µ₂-η¹:η¹), bridged, chelated and monodentated (2, µ₂-η¹:η¹, µ₁-η¹:η¹ and µ₁-η¹), or simultaneously bridged and chelated (3 and 4, µ₂-η²:η¹) coordination modes. Zn(II) centers accommodate coordination numbers 5 and 6, whereas Cd(II) presents coordination number 7. We have related their photophysical properties and fluorescence quantum yields with their geometric variations and interactions supported by TD-DFT calculations.     

Magnetically separable CoFe2O4/CoxFey/activated carbon composites for Cd(II) removal from wastewater

CoFe₂O₄ and Co_x Fe_y were anchored into activated carbon (AC) to synthesize CoFe₂O₄/Co_x Fe_y /AC composites using the sol–gel method for Cd(II) adsorption from wastewater. The results indicated that CoFe₂O₄ and Co_x Fe_y nanoparticles existed in the pores of AC. The magnetic properties of CoFe₂O₄/Co_x Fe_y /AC indicated it could be separated and retrieved easily using an external magnet after Cd(II) adsorption. The effects of solution pH, temperature and initial Cd(II) concentration on the Cd(II) adsorption of AC and CoFe₂O₄/Co_x Fe_y /AC were investigated. The standard free energy, enthalpy change and entropy change were evaluated. The kinetic parameters of Langmuir and Freundlich isothermal equation were analyzed, and the Freundlich kinetic model was feasible for describing the Cd(II) adsorption process of CoFe₂O₄/Co_x Fe_y /AC composites.     

Specific mercury(II) adsorption by thymine-based sorbent

A new kind of polymer sorbent based on the specific interaction of Hg(II) with nucleic acid base, thymine, is described for the selective adsorption of Hg(II) from aqueous solution. Two types of sorbents immobilized with thymine were prepared by one-step swelling and polymerization and graft polymerization, respectively. The maximum static adsorption capacity of the new polymer sorbents for Hg(II) is proportional to the density of thymine on their surface, up to 200 mg/g. Moreover, the new kind polymer sorbent shows excellent selectivity for Hg(II) over other interfering ions, such as Cu(II), Cd(II), Zn(II), Co(II), Ca(II) and Mg(II), exhibits very fast kinetics for Hg(II) adsorption from aqueous solution, and can be easily regenerated by 1.0 M HCl. It also has been successfully used for the selective adsorption of spiked Hg(II) from real tap water samples. This new thymine polymer sorbent holds a great promise in laboratory and industrial applications such as separation, on-line enrichment, solid-phase extraction, and removal of Hg(II) from pharmaceutical, food and environmental samples.     

Complexation of Zn(II), Cd(II) and Hg(II) with thiourea and selenourea: A 1H, 13C, 15N, 77Se and 113Cd solution and solid-state NMR study

Zinc(II), cadmium(II) and mercury(II) complexes of thiourea (TU) and selenourea (SeU) of general formula M(TU)₂Cl₂ or M(SeU)₂Cl₂ have been prepared. The complexes were characterized by elemental analysis and NMR (¹H, ¹³C, ¹⁵N, ⁷⁷Se and ¹¹³Cd) spectroscopy. A low-frequency shift of the C=S resonance of thiones in ¹³C NMR and high-frequency shifts of N–H resonances in ¹H and ¹⁵N NMR are consistent with sulfur or selenium coordination to the metal ions. The Se nucleus in Cd(SeU)₂Cl₂ in ⁷⁷Se NMR is deshielded by 87?ppm on coordination, relative to the free ligand. In comparison, the analogous Zn(II) and Hg(II) complexes show deshielding by 33 and 50?ppm, respectively, indicating that the orbital overlap of Se with Cd is better. Principal components of ⁷⁷Se and ¹¹³Cd shielding tensors were determined from solid-state NMR data.     

Novel Three-dimensional Sensor for Rapid Detection of Pb(II) and Cd(II) in Edible Mushrooms

A sensing platform was developed based on the molybdenum disulfide-reduced graphene oxide (MoS₂-RGO). The flower-like MoS₂-RGO nanocomposite had a large number of active sites such as oxygen-containing groups and highly reactive sulfur that contributed to the adsorption and preconcentration of heavy metal ions (HMIs). MoS₂-RGO was synthesized by one-step reduction method. Under optimized conditions, the limits of detection (LODs) for Pb(II) and Cd(II) was 0.13 μg/L and 0.59 μg/L with a linear range of 4.1–207.2 μg/L and 2.2–112.4 μg/L, respectively. The modified sensors had been successfully applied to detect Pb(II) and Cd(II) in three kinds of edible mushrooms.