云南铁矿资源现状及扩大远景途径

全省上表铁矿111处,总储量32.16亿吨,其中有11.27亿吨暂不能使用.而且,富铁矿少,难选矿多,分布边远,难以满足经济发展需求.必须解决菱铁矿、高磷矿选矿问题,以及有远景磁异常补充深部找矿问题,可望取得突破.     

有孔虫壳体内草莓状黄铁矿成因及其地质意义——以湖北雁门口地区栖霞组有孔虫化石为例

在湖北省京山县雁门口地区栖霞组上部的含泥灰岩中存在丰富的节房虫科底栖有孔虫化石,主要有节房虫属、厚壁虫属和郎格虫属,壳体均被草莓状黄铁矿充填。对其系统的显微镜、扫描电镜观察和黄铁矿的能谱分析结果发现,黄铁矿草莓体直径最大为15 μm,平均约10 μm,硫铁原子比值（S/Fe）为1.90±0.10,表明在黄铁矿形成过程中,有孔虫壳体空腔内呈轻度- 中度贫氧的微环境。在分析该类黄铁矿成因的基础上,认为有孔虫壳体内的黄铁矿在指示沉积环境和保存环境方面具有局限性。     

音频大地电磁测深在齐大山铁矿王家堡子采区深部找矿中的应用

鞍山齐大山铁矿王家堡子采区产出鞍山式沉积变质型铁矿,铁矿石多以磁铁贫矿为主,局部产出富铁矿,目前钻探工程控制标高为-600 m,采区深部的资源潜力是急待解决的问题,为此对采区进行音频大地电磁测量和研究工作。齐大山铁矿的电性变化复杂,通过先期的实验剖面确定了矿区铁矿体的3种不同电阻率特征,然后对王家堡子采区的3760线、4050线、4500线进行音频大地电磁测量、数据处理和断面反演分析。推测3760线的低阻由磁铁贫矿引起,局部高阻为假象赤铁贫矿引起;推测4050线和4500线浅部的低阻由磁铁贫矿引起,深部的高阻为假象赤铁贫矿及磁铁贫矿引起。同时预测3760线、4050线和4500线西侧深部均有低电阻率显示,反映出隐伏铁矿床的存在特征,推测在-1 000 m标高以下仍存在有隐伏的富矿体或板状磁铁贫矿。经过钻探验证,获得了预期的找矿效果。     

煤矿酸性矿井水主动式生物修复中铁的行为与归宿

酸性条件下Fe(II)的生物氧化过程可以被有效应用于煤矿酸性矿井水修复中,但是Fe行为与归宿的不确定性增加了应用难度。本研究通过对某煤矿酸性矿井水场地发生的生物地球化学过程进行监测,富集培养场地沉积物嗜酸微生物群落,进行室内恒化生物反应器连续流实验,探究微生物作用下Fe及其他金属离子的行为与归宿。研究表明,Fe的形态转化是场地和反应器中最主要的生物地球化学过程。当pH<2.7时,反应更倾向于产生溶解性Fe(III);当2.7Fe(III)。在酸性条件下,主动式生物反应器中其他金属离子并无明显形态转化。反应器中的沉积物主要由施氏矿物和针铁矿组成,并随着酸碱添加量的增加,向黄钠铁矾过渡。这些研究有助于将此类微生物过程应用于实际污染水体修复中,并为修复系统中的污泥回收和再利用提供科学依据。     

Basaltic and Solution Reference Materials for Iron,Copper and Zinc Isotope Measurements

Iron, Cu and Zn stable isotope systems are applied in constraining a variety of geochemical and environmental processes. Secondary reference materials have been developed by the Institute of Geology, Chinese Academy of Geological Sciences (CAGS), in collaboration with other participating laboratories, comprising three solutions (CAGS‐Fe, CAGS‐Cu and CAGS‐Zn) and one basalt (CAGS‐Basalt). These materials exhibit sufficient homogeneity and stability for application in Fe, Cu and Zn isotopic ratio determinations. Reference values were determined by inter‐laboratory analytical comparisons involving up to eight participating laboratories employing MC‐ICP‐MS techniques, based on the unweighted means of submitted results. Isotopic compositions are reported in per mil notation, based on reference materials IRMM‐014 for Fe, NIST SRM 976 for Cu and IRMM‐3702 for Zn. Respective reference values of CAGS‐Fe, CAGS‐Cu and CAGS‐Zn solutions are as follows: δ⁵⁶Fe = 0.83 ± 0.07 and δ⁵⁷Fe = 1.20 ± 0.13, δ⁶⁵Cu = 0.57 ± 0.06, and δ⁶⁶Zn = ?0.79 ± 0.12 and δ⁶⁸Zn = ?1.65 ± 0.24, respectively. Those of CAGS‐Basalt are δ⁵⁶Fe = 0.15 ± 0.07, δ⁵⁷Fe = 0.22 ± 0.10, δ⁶⁵Cu = 0.12 ± 0.08, δ⁶⁶Zn = 0.17 ± 0.13, and δ⁶⁸Zn = 0.34 ± 0.26 (2s).     

低聚合羟基铁离子-蒙脱石复合体吸附砷的实验研究

将提纯的钙蒙脱石与羟基铁离子溶液作用，制备了低聚合羟基铁－蒙脱石复合体，用化学分析，电子探针分析，粉晶X射线衍射分析，差热分析和穆斯堡尔谱分析等手段。对蒙脱石原样，低聚合羟基铁－蒙脱石复合体和相同条件下制备的铁的含水氧化物进行了表征。在实际土壤的酸度（pH=4-7)和温度（18－40℃）条件下，进行了低聚合羟基铁－蒙脱石复合体吸附有害元素砷的实验，探讨了复合体的砷吸附能力与pH值，温度，吸附时间，砷初始浓度，离子强度间的关系，并与蒙脱石和铁的含水氧化物的砷吸附行为进行了对比，研究表明，在实验条件下，低聚合羟基铁－蒙脱石复合体对砷具有明显的亲合力，低聚合羟基铁－蒙脱石复合体吸附砷的过程有可能是地表岩石和土壤中重要的地球化学过程，是影响砷地地表，特别是土壤中迁移，富集的重要因素。     

Absorption of Arsenite on Several Iron （Hydro-）Oxides and Impact from Pre-processing Methods

The absorption reactions of arsenite on Fe （hydro-）oxides are studied. The three absorbent types are Fe（OH）3 gel and two Fe （hydro-）oxides, in which the Fe（OH）3 gel was dried in a microwave oven under vacuum at 80℃. It is found that pH changes from 9.71 to 10.36 in 6 minutes after the Fe （OH）3 gel was mixed with NaAsO2 solution, as the arsenite replaces the OH- in goethite and Fe（OH）3. At the 40th minute after the start of the reaction, pH decreases, which is most probably because that the monodentate surface complex of absorbed arsenite has changed into mononuclear-bidentate complex and released proton. The decline in pH values indicates not the end of the absorption but a change in the reaction type. Temperature and dissolved gas has little effect on these two types of reactions. The total absorption of arsenite increases after the absorbent is irradiated with ultrasound, which also lead to difficulty in separating the solids from solution. The absorption capacity for arsenite of Fe（OH）3 gel dried in a microwave oven under vacuum is 53.18% and 17.22% respectively better than that of Fe （OH）3 gel and gel dried at 80℃. The possible reasons are that the water molecules in the gel vibrates with high frequency under the effect of microwave irradiation, thereby producing higher porosity and improved surface activity.     

利用碳酸盐岩的Fe/Mn比值恢复海洋的氧化还原状态

碳酸盐岩的Fe/Mn元素比值,作为一项新的地球化学指标,可以用于恢复海洋的氧化还原状态.在氧化条件下,Fe3+和Mn4+均不可溶,因此氧化海水中的溶解Fe和Mn的含量均很低.Fe3+和Mn4+在还原条件下可以被细菌还原为可溶的Fe2+和Mn2+,而氧化还原电位的计算表明,Mn4+的还原要早于Fe3+的还原,因此细菌的Mn还原过程发生在沉积物的更浅层.可溶的Fe2+和Mn2+向上扩散到海水中,替代碳酸盐岩晶格里的Ca2+,因此碳酸盐岩晶格中的Fe2+和Mn2+的含量受控于来自沉积物孔隙水的扩散,而后者又与水岩界面的氧化还原状态相关.因此可以预测,随着海水变得逐渐缺氧,碳酸盐岩中的Fe/Mn比值会逐渐增高.为了验证这一假说,我们分析了中元古代高于庄组白云岩的Fe/Mn比值.研究发现,几乎所有的样品的Fe/Mn比值介于20~30之间,显著高于泥盆纪末期深水碳酸盐岩和浅水台地碳酸盐岩的Fe/Mn比值.高于庄组碳酸盐岩高的Fe/Mn比值一方面可能指示了中元古代低的大气氧气浓度和海洋的广泛缺氧,也可能反映了白云岩形成于缺氧的沉积物空隙水里.     

长白山天池火山天文峰期黄色浮岩成因研究

长白山天池火口北侧天文峰之上,一套醒目的黄色浮岩引起广泛的关注,其颜色成因问题更是讨论的热点。本文通过野外地质调查、显微形貌和地球化学分析等方法,探索了黄色浮岩的颜色成因问题,并对此次喷发活动（天文峰期喷发）有了更进一步的认识。黄色浮岩与其下部灰白色浮岩应为同一期喷发所形成,两者成分一致且特征相似。黄色浮岩初始颜色为灰白色,后期受所处环境（降水丰富）与本身气孔特征的影响,浮岩内发生了元素析出和元素沉淀的过程。首先,浮岩内Si与H₂O结合形成弱硅酸（H₂SiO₃）,而大气中CO₂与H₂O结合形成弱碳酸（H₂CO₃）,在弱酸环境下火山玻璃逐渐析出Si、K、Al、Ca和Fe等阳离子,而析出的元素易溶于水的部分被流水带走,难溶于水的Fe与Al富集并粘附在火山玻璃壁上,同时由于Fe可与H₂O络合形成黄色的Fe的水合物（Fe₂O₃·nH₂O）,而Al与H₂O络合形成凝胶状白色水合物（Al₂O₃·nH₂O）,两者混合形成了黄色胶状物粘附在火山玻璃壁上,改变了浮岩原本的灰白色,形成了黄色浮岩。因此,天文峰期浮岩的黄色是由于后期风化淋滤作用所造成,属于次生色。本研究提高了对火山喷发堆积物风化淋滤作用过程的认识,也为其他地区相似颜色变化问题的讨论提供了借鉴。

     

Migration and enrichment of trace elements of Lower Palaeozoic carbonate rock strata in Beijing

Analyses of trace elements of the Lower Palaeozoic carbonate rock strata in Beijing show that the contents of As, Hg, F increase from primary carbonate rocks to weathered carbonate rocks and from primary carbonate rocks to the soil coexisting with carbonate rocks, but the distribution regularity of S is not obvious. In the whole weathered stages, the sorption of As is mainly affected by Fe2O3. In soil Fe2O3 is also the main affecting factor of Hg enrichment. The main existing forms of Hg in primary carbonate rocks should simply be physical adsorption, coprecipitation and false isomorphous form between surface of carbonate rock and Hg. In soil the enrichment of F has little relationship with sul-fides and Fe2O3. In primary carbonate rocks, F is mainly absorbed by sulfides and clay minerals, etc. Weathered samples have closer genetic relationships with primary carbonate rocks. This also implies that weathered carbonate rocks have the close existing forms to that of primary carbonate rocks. In primary carbonate rocks FeS2 and FeS are the main forms of S, and sulfides have fixation effect on some heavy metals, whereas in weathered carbonate rocks and soil the fixation effect is weakened.