壳聚糖与尿素的相互作用及其应用研究进展

尿素能够显著破坏甲壳素/壳聚糖分子氢键结构和疏水相互作用,增加其临界胶束浓度,促进多糖大分子的溶解,并能减少其在溶液中的自聚集现象.碱-尿素水溶液可以作为一种新型的甲壳素/壳聚糖绿色溶剂,有望用于对刺激性要求较为苛刻的食品、生物医学等领域.壳聚糖衍生物特别是其与过渡金属离子的配合物具有良好的尿素吸附功能,可用于尿毒症患者血液中小分子毒物的吸附,对机体刺激性小且不吸附血清蛋白等生物大分子.有望成为血液灌流治疗法中清除尿素等小分子毒性物质的良好吸附剂.壳聚糖还可以作为包膜材料,制备壳聚糖包膜尿素,与普通的包膜尿素相比性能更为优越.     

磁性壳聚糖微球的制备及对Cr(Ⅵ)的吸附性能研究

用壳聚糖包埋磁流体,用戊二醛交联制成磁性壳聚糖微球,并用红外光谱表征其结构。用制备的磁性壳聚糖微球吸附Cr(Ⅵ)离子,考察了其对Cr(Ⅵ)离子的吸附性能;探讨了吸附时间、溶液pH值、吸附剂用量、温度、Cr(Ⅵ)起始浓度以及其他离子存在对Cr(Ⅵ)离子去除率的影响。实验结果表明,磁性壳聚糖微球吸附Cr(Ⅵ)离子的最佳条件为:吸附平衡时间40 min,最佳吸附pH值6左右,磁性壳聚糖微球用量10 mg,温度升高有利于提高磁性壳聚糖微球的吸附效率,Cr(Ⅵ)离子起始质量浓度为12μg/mL,无机盐的存在引起磁性壳聚糖微球的吸附性能降低。并且考察了吸附剂的再生性能,实验结果表明磁性壳聚糖微球具有良好的重复使用性。     

尿毒症中分子毒物吸附剂的研究(Ⅲ)——酸性氨基酸修饰交联壳聚糖

以球状壳聚糖为载体,酸性氨基酸为配体,合成了尿毒症中分子毒物吸附剂,并测试了其血液相容性.为了研究吸附剂对尿毒症患者体内多肽蓄积物的吸附性能,选取分子量不同的6种多肽作为体内蓄积多肽的模拟物进行吸附实验.研究表明,吸附剂对多肽模拟物产生一定的吸附作用.在此基础上又对尿毒症患者血清超滤液进行了吸附实验,结果显示,吸附剂对血清中分子级分的清除率为10.3%.     

尿毒症中分子毒物吸附剂的研究——Ⅱ. 交联剂链长对壳聚糖树脂吸附性能的影响

用甲醛、乙二醛和戊二醛作为交联剂,以反向悬浮的方法制备了3种不同的交联壳聚糖树脂吸附剂,并对其中的后两种用NaBH₄进行了还原处理.经红外光谱表征和扫描电子显微镜观察,氢化还原处理有效地提高了吸附剂的化学稳定性;而交联剂的不同则对吸附剂的表面形态有着明显的影响.通过对尿毒症中分子毒物的模拟物和牛血清白蛋白的吸附研究发现,3种壳聚糖树脂吸附剂都在符合临床血液灌流要求的时间里达到了吸附平衡,在对牛血清白蛋白几乎不发生吸附作用的同时,其对模拟的中分子毒物则都产生了一定的吸附作用,但吸附量有所不同;随着交联剂脂肪链的增长,吸附剂对模拟的中分子毒物的吸附能力逐渐增强;以戊二醛为交联剂时,吸附剂的吸附效果最好.     

交联化羟丙基壳聚糖对Cr(Ⅵ)的吸附与结构分析

研究了交联化羟丙基壳聚糖对Cr(Ⅵ)的吸附作用,探讨了溶液的pH值、反应时间、温度、初始浓度等因素对其吸附性能的影响,并且用FTIR、XRD和SEM对吸附前后物质进行了表征与结构分析。实验表明,pH是交联羟丙基壳聚糖吸附Cr(Ⅵ)的主要影响因素。在pH=5时,对Cr(Ⅵ)初始浓度为15mg/L的溶液,可控制温度在20℃左右吸附2h,吸附剂交联羟丙基壳聚糖用量为1g/100mL溶液即能达到满意的吸附效果。吸附后由于交联羟丙基壳聚糖与Cr(Ⅵ)的配位作用使得交联羟丙基壳聚糖的结晶性明显降低;Cr(Ⅵ)的配位使得交联羟丙基壳聚糖的表面形貌发生了改变。     

浮石负载壳聚糖吸附去除水中丙溴磷

通过浮石负载壳聚糖制备了吸附剂壳聚糖/浮石复合物,采用扫描电子显微镜(SEM)、热重分析(TGA)、元素分析、傅里叶红外光谱(FT-IR)、X射线衍射(XRD)和X射线荧光光谱(XRF)等技术手段表征了吸附剂性质,考察了吸附剂量、吸附时间、溶液pH值、离子强度和温度对该吸附剂吸附去除水中丙溴磷的影响,研究了再生吸附剂的吸附性能。结果表明,负载在浮石上的壳聚糖占吸附剂总量的8.69%;在p H值3.0~7.0内,壳聚糖/浮石对丙溴磷的吸附率大于90%;这种吸附剂对丙溴磷的吸附受溶液离子强度影响较小,随温度升高而稍微减小。在溶液温度25℃、pH=7.0、丙溴磷浓度40 mg/L、壳聚糖/浮石剂量为0.7 g/L和吸附平衡时间为90 min条件下,此吸附剂对丙溴磷最大吸附率为93.3%(最大吸附量为53.4 mg/g)。壳聚糖/浮石连续经过3次吸附/再生循环,每次循环对丙溴磷的吸附率下降约12%。可见壳聚糖/浮石通过吸附可有效地去除水中的农药丙溴磷。     

壳聚糖及其改性衍生物对锆(Ⅳ)离子的吸附研究

壳聚糖经双氧水降解得到低分子量壳聚糖,用水杨醛对低分子量壳聚糖进行化学改性得到其相应的衍生物.分别研究了壳聚糖和水杨醛改性的低分子量壳聚糖对锆(Ⅳ)离子的吸附,考察了锆(Ⅳ)离子起始浓度、溶液pH值、吸附时间以及温度对这两种吸附剂吸附锆(Ⅳ)离子性能的影响,得出了最佳吸附条件.用红外对最佳条件下的吸附产物进行了表征.结果表明,壳聚糖吸附锆离子的最佳条件为:锆(Ⅳ)离子的起始浓度为6.5×10-4g/mL,振摇时间为6.5h,pH值为5～6;水杨醛改性的低分子量壳聚糖吸附锆离子的最佳条件为:锆离子的起始浓度为4.7×10-4g/mL,振摇时间为5h,pH值为5～6.这两种吸附剂对锆(Ⅳ)离子的吸附受温度影响均不大,吸附行为均满足Langmuir等温式.红外光谱分析表明,锆(Ⅳ)离子与这两种吸附剂均发生了配位作用.     

壳聚糖交联不溶性腐殖酸吸附剂的制备及其吸附性能

以壳聚糖和不溶性腐殖酸为原料,采用滴加成球法制备了一种新型重金属离子吸附剂——壳聚糖交联不溶性腐殖酸,对其进行了物理性质测定及FT-IR、SEM等分析。研究了吸附剂对水溶液中Pb(Ⅱ)的吸附特征。吸附等温线分别以Freundlich和Langmuir方程进行拟合,结果显示,吸附的最佳模型为Freundlich吸附模型。利用该方程拟合的数据,由Clausius-Claperyon’s方程计算出的Pb(Ⅱ)吸附焓变值,说明吸附剂对Pb(Ⅱ)的吸附以化学吸附为主。利用吸附剂吸附Pb(Ⅱ)前后的XPS分析了吸附机理,同时考察了温度、p H值及吸附时间对吸附效果的影响。结果表明,随着温度的升高和pH值的增大,吸附剂对Pb(Ⅱ)的吸附量增加,而且吸附更符合准二级动力学模型。     

新型吸附剂的合成、表征及其对Ni(II)的吸附研究

利用滴加法合成了球形含Ni2 交联壳聚糖,并通过胺化引入大量活性氨基,再经除镍制成对重金属镍离子具有较好吸附能力的新型吸附剂[P-C-CTS(Ni)].通过Ni2 吸附容量的测定,IR及XPS分析,验证了合成技术路线的正确性.通过研究pH值对吸附量的影响,初步讨论了无柠檬酸根(Cit)配位体存在时,吸附剂对Ni(II)的吸附为螯合作用.通过Cit存在条件下(cNi=cCit=0.852mmol·L-1),吸附剂对Ni(II)离子和Cit的吸附量随pH值的变化,结合相应pH值下金属镍的形态分布,探讨了其对Ni(II)的吸附机理,研究认为不仅仅是简单的螯合作用,其吸附机理和吸附量与溶液中金属离子的存在形式有关,引入静电吸附原理解释了吸附剂对Ni(II)的吸附现象.     

氨基酸修饰壳聚糖对胆固醇的吸附作用

通过将不同脱乙酰度的壳聚糖粉末与戊二醛交联,再经苯丙氨酸和色氨酸修饰,得到了两种珠状壳聚糖吸附剂,并进而研究了有关吸附剂对胆因醇的吸附性能。实验表明,交联壳聚糖珠对ＣＨＯ的吸附能力比壳聚糖粉末降低,而经不同氨基酸修饰后的壳聚糖珠对ＣＨＯ吸附能力提高,用Ｐｈｅ修饰比用Ｔｒｙ修饰的珠吸附性能更好些。     

尿毒症中分子毒物吸附剂的研究(Ⅰ)——戊二醛交联壳聚糖吸附剂

长期以来 ,血液净化疗法一直是临床上处理各种血液中毒的基本手段[1～ 3] .对尿毒症患者 ,目前普遍采用的治疗措施是对其进行定期的血液或腹膜透析 [1] 缓解病情 ;然而单纯血液透析疗法难以清除患者体内的中分子毒物 ,以致血液透析的患者体内 ,中分子毒物的积累会达到很高的程度 .因此 ,通过研制高效的中分子吸附剂 ,以血液灌流的方式清除中分子毒物 ,对于控制和治疗尿毒症具有重要意义 .据文献报道 ,体内蓄积的中分子毒物中肽类物质占了一定的比例[4～ 9] ,患者的许多顽固临床症状与这些毒物的体内蓄积密切相关 [1,10 ] .本课题组的研究结…     

Investigations on the adsorbents for uremic middle molecular toxins (Ⅱ)——Influences of crosslinking agent chain length on the adsorption capacities of crosslinked chitosan adsorbents

Chitosan resins, which clinically served as adsorbents in hemoperfusion therapy, were prepared with reversed-phase suspension methodology using three differently structured crosslinking agents, methanal, glyoxal and glutaraldehyde. And the glyoxal and glutaraldehyde crosslinked chitosan resins were reduced with NaBH4 afterwards. By analyzing the results from FTIR and SEM, it was found that the reduction treatment to the adsorbents efficiently improved the chemical stability of these chitosan resins, and the shifts in crosslinking agents exerted influences over the morphologies of the adsorbents obviously. After being put to use in the adsorption tests upon some model uremic middle molecular toxins and BSA in vitro, all three adsorbents demonstrated a fairly realistic adsorption capability to the model toxins but little to BSA. And the adsorption process reached the equilibrium in a clinically qualified short time. But the adsorption capacities of these adsorbents to the model toxins were quite different. It     

Investigations on the adsorbents for uremic middle molecular toxins (II)

Chitosan resins, which clinically served as adsorbents in hemo perfusion therapy, were prepared with reversed-phase suspension methodology using three differently structured crosslinking agents, methanal, glyoxal and glutaraldehyde. And the glyoxal and glutaraldehyde crosslinked chitosan resins were reduced with NaBH₄ afterwards. By analyzing the results from FTIR and SEM, it was found that the reduction treatment to the adsorbents efficiently improved the chemical stability of these chitosan resins, and the shifts in crosslinking agents exerted influences over the morphologies of the adsorbents obviously. After being put to use in the adsorption tests upon some model uremic middle molecular toxins and BSA in vitro, all three adsorbents demonstrated a fairly realistic adsorption capability to the model toxins but little to BSA. And the adsorption process reached the equilibrium in a clinically qualified short time. But the adsorption capacities of these adsorbents to the model toxins were quite different. It had been found that with the growing of fatty chain length of crosslinking agent, these adsorbents showed a gradually increased adsorption capacity to the model toxins, and the glutaraldehyde crosslinked chitosan resin behaved best.     

壳聚糖-Fe(Ⅲ)复合凝胶球去除磷酸根的影响因素与吸附机理

为改善当前环境水体中的磷污染现状,利用溶胶-滴定-真空冷冻干燥法制备了壳聚糖-铁(CS-Fe)复合凝胶球去除水中磷酸根。 对CS-Fe凝胶球的形貌结构进行了表征,研究了材料对磷酸根的吸附影响因素,并探索了反应机理。 结果表明,CS-Fe对磷酸根的吸附为自发、吸热、熵增过程;吸附过程符合拟一级动力学方程,吸附平衡时间为50 min;根据Langmuir模型计算最大吸附量为23.97 mg/g,脱附效率大于90%。 傅里叶红外光谱(FT-IR)、扫描电子显微镜-能量散射谱(SEM-EDS)、Zeta电势分析、X射线光电子能谱(XPS)等证明,CS-Fe形成利于磷酸根快速吸附的蜂窝状结构;吸附机理包含静电吸附和离子交换过程。 该吸附剂将金属化合物的吸附性能与壳聚糖大分子利于构建多孔材料的特点相结合,改善了吸附效果,球状材料更利于回收,避免二次污染,具有良好应用前景。     

Synthesis and Properties of Surface Molecular Imprinting Adsorbent for Removal of Pb<Superscript>2+</Superscript>

A new chitosan imprinting adsorbent using diatomite as core material was prepared by using the surface molecular imprinting technology with the Pb²⁺ as imprinted ion. The preparation process conditions of the surface molecular imprinting adsorbent were studied. The adsorbent was characterized by using Fourier transform infrared (FTIR) spectrum. FTIR spectrum indicated that it was cross-linked by epichlorohydrin. The new imprinting adsorbent could provide a higher adsorption capacity for Pb²⁺, which reached 139.6 mg/g increasing 32.3% compared with cross-linking chitosan adsorbent (the initial Pb²⁺ concentration of 600 mg/L). The adsorption velocity was quick and the equilibration time of the imprinting adsorbent for Pb²⁺ was 3 h that shortened about 40% compared with cross-linking chitosan adsorbent. It had a more wide pH range of 5–7 than that of cross-linking chitosan adsorbent. The new imprinting adsorbent can be reused for up to ten cycles without loss of adsorption capacity. In the kinetics and isotherm study, the pseudosecond order model and Langmuir model could represent the adsorption process.     

Adsorption of tannic acid, humic acid, and dyes from water using the composite of chitosan and activated clay

Chitosan is a well-known excellent adsorbent for a number of organics and metal ions, but its mechanical properties and specific gravity should be enhanced for practical operation. In this study, activated clay was added in chitosan slurry to prepare composite beads. The adsorption isotherms and kinetics of two organic acids (tannic acid, humic acid) and two dyes (methylene blue, reactive dye RR222) using composite beads, activated clay, and chitosan beads were compared. With composite beads as an adsorbent, all the isotherms were better fitted by the Freundlich equation. The adsorption capacities with composite beads were generally comparable to those with chitosan beads but much larger than those with activated clay. The pseudo-first-order and pseudo-second-order equations were then screened to describe the adsorption processes. It was shown that the adsorption of larger molecules such as tannic acid (MW, 1700 g mol(-1)), humic acid, and RR222 from water onto composite beads was better described by the pseudo-first-order kinetic model. The rate parameters of the intraparticle diffusion model for adsorption onto such adsorbents were also evaluated and compared to identify the adsorption mechanisms.     

A NOVEL METAL CHELATE AFFINITY ADSORBENT FOR PROTEIN UPTAKE

1. INTRODUCTION Chitosan is a hydrolyzed derivative of chitin and belongs to a family of linear unbranched polysaccharides which contain large amounts of 1,4-linked-2-amino-2-deoxy-β-D-glucan residues. The presence of free amine groups in chitosan enhances the solubility and reactivity of this polymer. Interest in modifying chitosan by using glutaraldehyde has recently increased. The derivatized polymers have been employed for many applications [1~2], including protein immobilization…     

A Modified Chitosan Adsorbent for Selective Removal of Low Density Lipoprotein

A modified chitosan adsorbent was synthesized through a simple preparation procedure,and it demonstrated good adsorption performance for selective removal of low density lipoprotein in human plasma. Phase inversion technique was employed to form chitosan beads, to which epoxy groups were then introduced by reacting with ethyleneglycol diglycidylether, and tryptophan was subsequently coupled to the epoxy-activated beads.