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1.
Cu2+和Cd2+在蒙脱石-胡敏酸复合体上的吸附及其竞争 总被引：1，自引：0，他引：1
土壤和水体中的腐殖酸常常与粘土矿物紧密结合成为特殊的复合体.这种粘土矿物-腐殖酸复合体对重金属的吸附作用既有别于粘土矿物,更有别于腐殖酸.以蒙脱石和胡敏酸分别作为粘土矿物和腐殖酸的代表,通过一系列实验研究了Cu2+、Cd2+在单一体系和共存体系条件下在蒙脱石-胡敏酸复合体上的吸附作用,同时探讨了二者的竞争特点.实验结果表明,在单一体系条件下,蒙脱石-胡敏酸复合体对Cu2+的吸附量始终明显大于Cd2+,且二者的吸附量均随其初始浓度的增大而呈线性增大;而在Cu2+和Cd2+共存体系条件下,Cu2+的吸附量始终略大于Cd2+的吸附量,即复合体对Cu2+的吸附有较好的选择性.在吸附过程中,复合体中的蒙脱石与Cd2+和Cu2+的阳离子交换作用处于主导地位.无论是在单一体系还是在共存体系中,Cd2+优先替换电价相同而半径略大的Ca2+,而Cu2+则优先替换半径相近、电价低的Na+.因此,Cd2+的存在使Cu2+在复合体上的吸附量明显地减小,而Cu2+的存在对Cd2+的吸附几乎没有影响.这些实验结果将有助于深入探讨重金属离子在土壤、水体等环境中的迁移-固定行为. 相似文献
2.
高岭石和蒙脱石分别是暖湿和冷干气候带内典型土壤的代表性矿物,对二者吸附胡敏酸特点的对比研究可以为探索不同地带土壤中重金属的环境行为提供重要的依据。笔者通过一系列实验研究了pH值、离子强度和胡敏酸初始浓度对胡敏酸在高岭石和蒙脱石上吸附量的影响,重点剖析了引起高岭石和蒙脱石在吸附胡敏酸方面表现出的共性和差异的原因。研究结果表明:1)在pH=5条件下,胡敏酸在高岭石和蒙脱石上的吸附量均随着胡敏酸初始浓度和离子强度的升高而逐渐增加;2)胡敏酸在高岭石和蒙脱石上的吸附量均随着pH值的升高而降低;3)pH<6时,高岭石吸附的胡敏酸量多于蒙脱石,pH>6时则相反。这是由高岭石和蒙脱石在不同pH条件下吸附胡敏酸的机制不同造成的。在pH<6时,高岭石与胡敏酸之间的静电引力起主导作用,其次是配位交换作用和氢键作用。此时,蒙脱石以氢键作用为主要吸附机制。在pH>6时,高岭石和蒙脱石的主要吸附机制分别是疏水性作用和阳离子键桥。 相似文献
3.
蒙脱石/胡敏酸复合体对重金属离子吸附实验研究 总被引：2，自引：0，他引：2
主要研究了蒙脱石吸附胡敏酸后形成的复合体对Cu2 、Cd2 、Cr3 3种重金属离子的吸附.实验结果表明:用胡敏酸对蒙脱石改性后能提高其对3种重金属离子的吸附性能,胡敏酸浓度越大,吸附性能提高程度越大,3种重金属离子的Langmuir吸附等温线线性相关都能达到0.99以上.蒙脱石/胡敏酸复合体对3种重金属离子的吸附量都随pH值的升高而增加,随离子强度的增加而减小.另外还对其吸附动力学进行了研究,发现可用Elovicb方程和双常数方程对吸附过程进行较好地拟合. 相似文献
4.
以皂石、高岭石、绿泥石和伊利石为原材料,分别与赖氨酸进行反应,研究赖氨酸在上述粘土矿物上的吸附行为,
并运用粉末X-射线衍射技术（XRD）、傅里叶变换红外吸收光谱术（FTIR）和热重（TG）等分析方法,表征反应前后粘土
矿物的变化。实验结果表明,不同粘土矿物对赖氨酸的吸附等温线均符合Freundlich等温方程,且不同粘土矿物对赖氨酸的
饱和吸附量大小顺序为：皂石>蒙脱石>绿泥石>高岭石>伊利石;XRD结果表明皂石对赖氨酸的吸附发生在矿物层间,而绿
泥石、高岭石和伊利石对赖氨酸的吸附主要在矿物表面进行;FTIR和TG结果表明赖氨酸主要取代粘土矿物层间吸附水,以
氢键的形式与Si-O-Si(IVAl)键合。实验结果将有助于进一步探明环境中粘土矿物对有机质的吸附机理。 相似文献
5.
镉在蒙脱石等粘土矿物上的吸附行为研究 总被引：5，自引：0，他引：5
研究了土壤中主要硅酸盐粘土矿物蒙脱石、伊利石、高岭石、海泡石对重金属镉的吸附行为.结果表明:硅酸盐粘土矿物吸附镉受酸度和离子强度的影响;吸附反应是快反应,能很好地符合Lagergren二级吸附速度方程;优化条件下的高岭石对镉吸附很弱,蒙脱石、伊利石、海泡石对镉的实验饱和吸附容量分别为2.88、1.08、2.82 mg/g,蒙脱石吸附镉更适合Freundlich拟合,伊利石、海泡石对镉的吸附结果更适合Langmuir拟合;相关性分析表明,硅酸盐粘土矿物对镉的饱和吸附容量大小与其理化性质有关,其中矿物中氧化锰含量高低与其对镉饱和吸附容量大小的相关性达到极显著水平. 相似文献
6.
页岩气储层粘土矿物孔隙特征及其甲烷吸附作用 总被引：3，自引：0，他引：3
粘土矿物是页岩的主要组成矿物,与页岩气的赋存和富集密切相关。粘土矿物因其特殊的晶体结构,在晶层之间、矿物内部以及矿物颗粒之间形成了不同类型的孔隙,这些孔隙的大小、形貌和比表面积决定着粘土矿物的甲烷吸附能力。为此,本文综述了粘土矿物的孔隙结构以及孔隙中的水和有机质对甲烷吸附性的影响,指出不同类型的粘土矿物孔隙发育与形貌特征存在差异,蒙脱石中多发育圆形、狭缝状的微孔且总比表面积最大,导致蒙脱石在所有粘土矿物中的甲烷吸附量最大;伊利石与高岭石中多发育中孔与大孔,吸附甲烷的能力低于蒙脱石。粘土矿物孔隙中的水与有机质显著影响到甲烷的吸附能力,水分子会占据孔隙表面,降低了甲烷的吸附能力,但可溶有机质对粘土矿物甲烷吸附能力的具体影响目前尚不明了。同时,根据页岩气勘探需求指出了本方向某些有待深入探讨的问题。 相似文献
7.
8.
几种粘土矿物对Pb^2＋的吸附作用及其主要影响因素的探讨 总被引：10，自引：0，他引：10
对土壤中常见的三种粘土矿物对Ｐｂ＾２＋的附作用及其主要影响因素进行了探讨。结果表明，三种粘土矿物对Ｐｂ６２＋的吸附能力顺序为：蒙脱石－伊利石－高岭石．蒙脱石对Ｐｖ＾２＋的吸附受ＰＨ的强烈影响，ＰＨ高有利于Ｐｂ＾２＋的吸附。与蒙脱石形成复合体形式的有机化合物的存在不利于蒙脱石对Ｐｂ＾２＋的吸附。 相似文献
9.
环境污染物在蒙脱石层间域中的环境化学行为 总被引：1，自引：0，他引：1
天然蒙脱石层间阳离子通常是Ｃａ2 +,Ｎａ+,可以通过离子交换法制备各种阳离子交换蒙脱石。这些不同阳离子对蒙脱石层间域的环境化学行为有着不同的影响。金属阳离子与粘土矿物间的相互作用除了离子交换外 ,粘土的专性吸附作用有时也是非常重要的。目前 ,粘土矿物对重金属离子的专性吸附可概括为 4种机理 :(1)重金属离子与粘土矿物表面或断键基团质子的交换吸附 ;(2 )重金属离子进入粘土矿物硅氧四面体片的复三方空位或八面体片晶格缺陷中 ;(3)以金属络合物形式的专性吸附 ;(4)以金属氧化物或其它不溶性盐类沉淀形式。天然粘土矿物存在着大… 相似文献
10.
粘土矿物对形成过渡带气的催化作用研究 总被引：1，自引：0，他引：1
本文分析了有机质在粘土矿物中的赋存状态，测定了粘土矿物的表面酸、实验模拟了低演化程度的烃源岩及其抽提物干酪根＋不同粘土矿物的催化机制、并通过粘土催化醇脱水反应对粘土过渡带有机质成气机理进行了探讨。研究结果表明，过渡带气的形成主要是受蒙脱石粘土矿物的催化所致，其原因是成岩过程中蒙脱石向混层矿物转化在蒙脱石晶间发生大量的铝代硅，因此在粘土表面产生电荷不平衡而形成酸性，井以路易斯酸和布郎酸作用于有机质，使碳－碳键发生断裂以形成气态烃。 相似文献
11.
为探讨天然黏土矿物及有机质对纳米乳化油在多孔介质中迁移滞留的影响，本文选取高岭石和蒙脱石这两种黏土矿物以及有机质的典型代表腐殖酸，开展了单一矿物、有机质及有机矿质复合物对纳米乳化油的吸持批实验研究，并运用比表面积全分析、扫描电镜(SEM)、傅里叶红外光谱(FTIR)、X射线衍射(XRD)等技术手段探讨了吸持机理。实验结果表明，介质对纳米乳化油的吸持均符合Freundlich模型；单一矿物及腐殖酸对纳米乳化油的吸持能力表现为：蒙脱石>腐殖酸>高岭石，有机矿质复合样品的吸持能力表现为：蒙脱石-腐殖酸>高岭石-腐殖酸，且均大于其对应的单一样品，出现了“1+1>2”的现象，表明介质组成越复杂，对纳米乳化油的吸持滞留程度越大。进一步分析证实，纳米乳化油主要通过氢键和疏水作用吸持在矿物和腐殖酸表面，表面结构性质是高岭石和蒙脱石吸持过程中的主导因素，因此蒙脱石具有更强的吸持能力，而腐殖酸的吸持主要通过颗粒间聚集作用来实现；对于复合样品，吸持主要通过氢键、配体交换和疏水作用结合来实现。腐殖酸与矿物的复合会增加吸持位点并且增强矿物表面疏水性，从而促进吸持。腐殖酸与纳米乳化油的共吸... 相似文献
12.
The adsorption of three copper species, the hydrated cupric ion, bisglycine Cu(II) and a Cu(II)-humic acid complex, on montmorillonite and imogolite at pH 7 was investigated by electron paramagnetic resonance (EPR) spectroscopy. The spectra of the supernatant solutions indicated that adsorption of the glycine complexes was very much less than that of the uncomplexed ion for both minerals and that montmorillonite adsorbed significantly more Cu from the humic acid solution than did imogolite. In every case the adsorbed Cu was characterized by more than one type of chemical environment and the spectral parameters show differences between the adsorbed species depending on their freedom of movement and their mode and site of adsorption. Qualitatively similar spectra were obtained when the uncomplexed ion was adsorbed on either of the mineral species and it is suggested that simple Cu(II) ions were involved and that their coordination environments comprised water molecules and hydroxyl groups. With the bisglycine Cu(II) complexes, the spectra were characterized by two components which may be accounted for by adsorption at two different types of site in the structures. In each case one component had parameters that are similar to those of the bisglycine Cu(II) in the solid state, but the second component in the spectra of the montmorillonite sample was quite different to that obtained with imogolite. The Cu(II)-humic acid complex with montmorillonite gave spectra that were similar to that from copper humate, but with imogolite the spectra from the Cu(II)-humic acid system were similar to those obtained with the uncomplexed Cu(II) ion, indicating that imogolite is able to extract copper from humic acid. 相似文献
13.
14.
Adsorption of antimony(V) on kaolinite as a function of pH,ionic strength and humic acid 总被引：1，自引：0，他引：1
The present work investigated the adsorption and mobility (desorption) of Sb(V) on kaolinite using batch experiments. The
adsorption of Sb(V) on kaolinite was studied as a function of contact time, pH, ionic strength, humic acid (HA), initial Sb(V)
concentration and temperature. Kinetic studies suggest that the equilibrium is achieved within 24 h. The adsorption of Sb(V)
was strongly affected by changes in I at low ionic strength and unaffected at high ionic strength. The adsorption is weakly
dependent on the presence of humic acid, but is strongly dependent on pH. Within the range tested, the optimal pH for Sb(V)
adsorption is 3.6, and close to 75% removal can be achieved. Desorption is dependent on the original suspension pH. The addition
sequence of Sb(V)/HA do not influence the adsorption of Sb(V) on kaolinite. The adsorption data fit both the Freundlich and
Langmuir isotherm. The thermodynamic parameters (ΔH
0, ΔS
0 and ΔG
0) were calculated from the temperature dependence, and the results suggest the endothermic and spontaneous nature of the process. 相似文献
15.
天然有机质和不同pH环境对纳米黑炭的迁移行为影响及作用机制 总被引：1，自引：0，他引：1
作为典型的黑炭,近年来生物炭的应用发展受到人们广泛关注。由于生物炭施加在土壤中,在表生地球化学长期作用下,会有部分逐渐破碎变小,直至微米、纳米级别,在土壤或水体中迁移,因此,对生物炭、特别是活性更强的纳米级生物炭的迁移性研究具有十分重要的意义,而关于纳米级生物炭的迁移性研究目前十分匮乏。通过石英砂柱中纳米生物炭的柱迁移实验,获得天然有机质和不同pH值(4、7、10)条件下的穿透曲线和空间滞留曲线,研究影响作用机制。结果表明：天然有机质(腐殖酸)能增强纳米生物炭的迁移性,中碱性pH环境也有助于其迁移。一方面纳米炭的分散性得到改善,另一方面腐殖酸和碱性环境有助于增加纳米炭和石英砂介质的颗粒表面负电荷,增大Zeta电位值(负值),从而使颗粒间静电排斥力增强,有助于纳米炭的迁移。研究结果对深入理解生物炭在自然界中地球化学迁移行为及其吸附污染物后的潜在迁移风险具有重要意义。 相似文献
16.
Shuji TAMAMURA Tsutomu SATO Yukie OTA Ning TANG Kazuichi HAYAKAWA 《《地质学报》英文版》2006,80(2):185-191
The fate of Polycyclic Aromatic Hydrocarbons （PAHs） residing in the atmosphere has received enormous attention in recent years due to their mutagenic and carcinogenic risks on human health. In this context, the stability of pyrene （as a representative PAHs） on quartz, alumina, montmorillonite, kaolinite, humic acid and quartz coated with sorbed humic acid was investigated at controlled relative humidity （RH： i.e. 5% and 30%） without light irradiation in order to detect the presence of catalytic effect of mineral surface on PAHs decomposition. The stability of pyrene was found to depend strongly on the physicochemical properties of the substrates. Quartz showed a strong catalytic effect for the decomposition of pyrene even though it was coated with sorbed humic acid. Pyrene sorbed on montmorillonite and humic acid remained stable during the experimental period （i.e. 3 days）. Moisture in the experimental cell also affected the stability of pyrene in particular minerals. Especially, pyrene sorbed on alumina was rapidly decomposed at higher RH. However, there were almost no effect in the case of quartz, kaolinite and humic acid. Depending on the physicochemical properties of aerosols and RH, PAHs associated with minerals in the atmosphere would be decomposed and/or stably reside in the atmosphere. 相似文献
17.
Chemical interactions between 2-aminobenzothiazole (ABT) and a soil humic acid (HA) extracted from a gleyic planosol were investigated by solid-state 13C CP/MAS NMR spectroscopy. Reactions of the HA with ABT 13C-labelled at the C-2 position were performed in aqueous solution under noncatalysed and enzyme-catalysed conditions. Without enzymic catalysis the amount of ABT-2-13C taken up by soil HA in an oxygen atmosphere was about twice the uptake under argon. In the presence of the oxidative enzyme laccase and air, about three times as much ABT was bound to HA as compared to the uptake in a control experiment with inactivated laccase. The results suggest that oxidation reactions of the humic acid significantly enhance the extent of binding between ABT and HA. The 13C NMR spectra of the HA–ABT adducts indicated that in both noncatalysed and enzyme-catalysed reactions ABT may be bound to humic acid by noncovalent as well as covalent bonds. 相似文献
18.
动态光散射技术原位表征天然有机质存在下纳米零价铁的团聚效应 总被引：1，自引：1，他引：0
纳米零价铁原位修复地下水污染是近年发展起来的新技术,通过改性合成不同种类纳米零价铁可以克服其易团聚易氧化的问题,水体中存在的天然有机质也会对纳米铁的分散性和反应活性产生影响,因此开展原位测试并研究不同种类纳米铁在水中的团聚效应具有重要意义。本文对实验合成的纳米零价铁、羧甲基纤维素包覆纳米零价铁、膨润土负载纳米零价铁以及商用纳米零价铁,基于动态光散射技术(DLS),运用纳米粒度/Zeta电位分析仪,结合透射电子显微镜(TEM)和沉降光谱曲线等手段,对比研究了天然有机质(腐植酸HA)对纳米铁团聚效应的影响。结果表明,羧甲基纤维素包覆或膨润土负载改性提高了纳米零价铁颗粒的分散稳定性,有效抑制了团聚沉降,团聚体粒径分布在1000 nm以下。HA会吸附在纳米铁颗粒表面,从而增加静电排斥力,进一步减缓了团聚效应,尤其是对膨润土负载纳米零价铁的影响最为显著,其团聚体粒径能降至100 nm以下,沉降速率也极大减缓,分散稳定性表现最佳。本研究表明DLS结合TEM表征纳米颗粒是获得更加丰富的微观粒子信息的一种非常重要的手段。 相似文献
19.
Humic acid adsorption onto the bacterial surface of Bacillus subtilis was measured with and without Cd, as a function of pH and humic–bacteria–Cd ratios. These experiments tested for the existence of ternary interactions in a bacteria–humic–metal system. We determine both the effects of humic acid on the bacterial adsorption of Cd, as well as the effects of the aqueous metal cation on the bacterial adsorption of humic acid. The presence of Cd does not affect the extent of humic acid adsorption onto the bacterial surface, indicating that there is no competition for sorption sites between humic acid and Cd under the experimental conditions, and that changes in the charging properties of the bacterial surface, as a result of the Cd adsorption, are not significant enough to affect humic acid adsorption.
The presence of humic acid does diminish Cd adsorption onto the bacterial surface, suggesting the presence of an aqueous Cd–humate complex under mid to high pH conditions. However, we also observe that the solubility of humic acid is unaffected by the presence of aqueous Cd. This apparently inconsistent behavior of an aqueous Cd–humate complex affecting Cd adsorption but not affecting humic acid solubility is not observed with simpler ionizable organic molecules. We propose that the solubility of humic acid is controlled by the solubility of a less soluble fraction of the acid. Cd forms an aqueous complex with the more soluble fraction of humic acid and there is no interdependence between the aqueous activities of the more and less soluble fractions. That is, the solubility of one humic acid fraction is unaffected by the presence of an aqueous Cd–humate complex involving another humic acid fraction. These experimental results constrain the relative importance of surface ternary and aqueous metal–humate complexes on the bacterial adsorption of both humic acid and metal cations. 相似文献