四川龙门山马角坝组铁质鲕粒成因及沉积环境

本文应用显微镜和扫描电镜对下石炭统马角坝组顶部的铁质鲕粒的研究发现:铁质鲕粒由核心和同心圈层组成,核心成分主要是赤铁矿碎屑和石英颗粒,圈层厚度较小,整体呈胶状形态,由赤铁矿围绕核心呈致密板状平行排列,整体上结构一致;铁质鲕粒是在适合的pH、Eh条件下,大量铁质围绕石英碎屑或矿物碎屑转动时胶体沉积形成的,沉积环境为潮间-潮下的浅水动荡环境,是大规模海退暴露后海平面初始上升期的产物。     

巢湖的稀土元素地球化学特征

采用液-液萃取法和ICP-MS测试技术对巢湖的溶解态稀土元素进行了分析。结果表明,巢湖的溶解态稀土的含量与世界淡水相当,丰水期的样品含量高于其他季节。pH值和悬浮物、胶体是控制巢湖水体中溶解态稀土含量的主要因素。巢湖的溶解态稀土的分布模式以平坦型为主,少数呈现重稀土富集。丰水期和枯水期的溶解态稀土的(La/Yb)N值从西半湖区到东半湖区呈现有规律性的逐渐增大,并且丰水期的(La/Yb)N值低于枯水期。在富营养化湖泊中,胶体和水生生物可能是造成这一现象的主要原因。     

滨海地下水交互带中的胶体运移行为研究综述

在分析国内外已有研究的基础上,综述滨海地下水交互过程中的胶体运移规律,重点阐述咸淡水驱替作用下胶体的宏观运移规律和微观作用机理。胶体在滨海地下水交互中可成为联系海-陆相的物质传输纽带,其运移行为主要受地下水水化学参数波动影响,受控于胶体类型与数量、表面电位及地下水pH、离子强度等因素,具有水动力、水环境多因子联合作用的特征,并在含水层中具有空间堵塞和团聚体结构改变的不确定性。未来关于滨海地下水交互带中的胶体行为研究应重视基础勘察,考虑胶体群体效应,结合滨海含水层对水动力、水化学条件的敏感性,研究胶体在多相体系中胶体运移的不确定性及其对污染物的协同运移作用,为滨海资源化研究构建统一分析体系和预测机制。     

密闭胶体取样技术的研究与应用

在硬、脆、碎地层取样过程中,使用常规取样钻具取样常会出现取心率低、岩心品质差的现象,为此特别设计了密闭胶体取样工具。在内蒙古野外现场实践过程中取心率提高至85%以上,获得了良好的效果。介绍了钻具的结构和设计原理,及其野外生产试验效果。     

高分子保护金属铜胶体催化剂的制备

研究了无氮气保护下胶体铜催化剂的制备方法和反应条件,在聚乙烯吡咯烷酮(PVP)保护下,用水合肼还原CuCl2,在80℃和pH=7.0±0.5条件下,可制得比较稳定的胶体铜溶液。改变PVP的分子量或PVP/Cu2 的摩尔比,可制得不同粒度的金属胶体铜。保护剂PVP的分子量越小,PVP/Cu2 的摩尔比越大,所得胶体铜粒径越小。用所得的胶体铜催化丙烯腈水合制备丙烯酰胺具有很高的活性。     

锂皂石—吡啶硫酮锌复合止痒去屑剂的研制及其在洗发香波中的应用

对锂皂石—ＺＰＴ复合止痒去屑剂应用于洗发香波作了研究,利用锂皂石胶体解决了ＺＰＴ稳定、不沉淀的介质问题。产品具有明显的去屑止痒作用,有很好的应用价值。     

Separation of nano-colloids in soils

The study of the physicochemical behaviour of colloids and particles in nature has emerged as a scientific problem of critical importance because of the widespread acknowledgement of their significance in controlling the speciation and fate of essential nutrients and contaminants in the aquatic and soil environments （Ledin et al., 1995; Lead et al., 1999, Doucet et al., 200 l; McCarthy et al., 1989; Koterba et al., 1993; Kretzschmar et al., 1999）. Se＇quaris and Lewandowski （2003） developed a method based on sedimentation and centrifugation steps to fractionate agricultural top soils after suspension in water. However, progress in the field has been limited by the lack of appropriate techniques for the isolation and characterization of colloids and particles in their native form （Lead et al., 1997）. The primary difficulties in separation and analysis are colloidal instability and their small size and low concentration. As a result, reliable, unbiased and minimally perturbing methods for sampling and fractionation are primary requirements for the study of colloids and particles if valuable information is to be obtained. In recent years, cross-flow ultra-filtration （CFUF） has become one of the most commonly used techniques for collecting and separating freshwater and marine colloids and particles （Petrus evski et al., 1995; Gustafsson et al., 1999; Benoit et al., 1999; Sigg et al., 2000; Gue＇guen et al., 2002; Benedetti et al., 2003）. CFUF has hitherto been used for studies of the biogeochemical cycling of a variety of elements, such as carbon （Benner et al., 1992; Santschi et al., 1998）, radionuclides （Moran et al., 1992）, trace metals （Reitmeyer et al., 1996） and nutrients （Bauer et al., 1996）. The purpose of this study was to develop a protocol to fractionate particles in soil, to measure particle size distributions and to quantify chemical characteristics within different particle size fractions.     

广东海南岛石碌铁矿石英的研究及其意义

本文在显微镜研究基础上,综合运用扫描电镜、光谱分析、X射线分析、差热分析和红外光谱等手段,对铁矿中石英进行矿物标型特征的研究。论证了这种石英的绝大多数有蛋白石→玉髓→石英的形成过程。同时,成矿时也很可能有一些火山成因石英斑晶或晶屑掺杂其中,而陆源碎屑石英少见。还发现了铁矿中玉髓的似生物结构。因而为石碌铁矿海相火山(胶体)沉积变质成因说提供了新的科学依据。     

Metal ions bound to colloids from database to field systems

Nowadays, environmental problems related to soil pollution with heavy metals are numerous, therefore, it is important to understand metal behavior in aquatic sediments and soils and to appreciate their transfer. The fate of the metals in the environment is closely related to their interactions with the major reactive compartments （organic matter, iron and manganese oxides, clays）. The objective of this work is to develop an approach based on the combination of several models to study metal ion speciation in different environmental systems. Models used to describe the interactions of metals with the main reactive phases in the soil are CD-MUSIC （amorphous and crystallized iron oxides）, NICA-Donnan （organic matter and manganese oxides）, and cationic ion exchange model （clays）. Firstly, this work implies the definition of generic parameters to describe the interactions of the studied metals with iron and manganese oxides, a part of this information is missing in the literature. Then, after the validation of the approach by comparison with analytical results, this multi-surface model is applied to test sites corresponding to a soil and to two riverine environments. These new models give good predictions of the behavior of major and trace metal ions even in heterogeneous system characteristics of the natural environment. The measured free metal concentrations in the solution are in agreement with those obtained from model calculations.