安徽庐枞盆地罗河铁矿床中榍石LA-ICP-MS U-Pb定年及其意义

罗河铁矿床位于长江中下游铁铜金成矿带庐枞矿集区,已探明资源量约10亿吨,是成矿带内最大的铁矿床。矿床主成矿阶段广泛发育热液成因榍石,以榍石-硬石膏-磷灰石组合为特征,在矿床-800~-900m和-1500~-1600m两个不同深度稳定发育,为确定成矿时代和成矿流体演化提供了良好的研究对象。本次工作对罗河铁矿床深部和浅部两层矿体中热液榍石开展了年代学及地球化学研究,结果表明榍石中存在(Al,Fe)~(3+)+(F,OH)~-=Ti~(4+)+O~(2-)置换反应,并富含Zr、Nb和REE等元素。榍石中Zr含量估算矿床成矿温度约700℃,指示玢岩型矿床比矽卡岩型铁矿床具有更高的成矿温度,高温条件有利于Ti元素的迁移。榍石的稀土元素配分图均呈现出明显右倾,并具较高的稀土元素总量以及明显的负Eu异常特征,轻稀土富集表明其结晶早于磷灰石和绿帘石等矿物,形成于高温热液环境,不同深度榍石的Eu异常变化表明成矿流体的氧逸度从深部到浅部有所升高。热液榍石原位微区LA-ICPMS U-Pb定年结果表明,上、下两层榍石形成时代分别为130.0±0.9Ma和129.1±0.8Ma~129.7±0.8Ma,表明罗河铁矿床两层矿体是同一成矿系统的在不同深度的产物。矿床成矿时代与区内隐伏闪长岩体成岩时代一致,结合矿床地质特征研究,本文认为闪长玢岩是矿床的成矿母岩。罗河铁矿床属于燕山晚期岩浆热液活动的产物,形成于区域早白垩世岩石圈减薄的环境。     

57Fe Mössbauer spectroscopy of tektites

Tektite glasses are investigated using ⁵⁷Fe Mössbauer spectroscopy. Room temperature spectra analysis is performed using two complementary analytical methods based on two-dimensional distributions of both isomer shift and quadrupole splitting. No a priori correlation between the two hyperfine parameters is considered. The first method, based on a shape independent distribution, provides the justification for the Gaussian distribution shape used in the second method. No ferric iron contribution is evidenced by Mössbauer spectra analysis in these samples, although several criteria are used. Ferrous iron sites are shown to be continuously distributed between four- and five-fold co-ordinated sites.     

典型喀斯特地区马尾松纯林及马尾松-阔叶树混交林营养元素生物循环研究——以贵州龙里为例

以龙里典型喀斯特地区马尾松纯林及马尾松-阔叶树混交林为研究对象,研究了两个群落的生物量、营养元素贮量、分布及循环特征.结果表明:马尾松纯林、马尾松-阔叶树混交林的生物量分别为40.62t/hm2、48.32t/hm2,混交林的乔木层总生物量比马尾松纯林高18.97%,根系生物量较纯林高65.12%.混交林乔木层各器官营养元素的含量整体大于马尾松纯林,两群落乔木层N、P、K、S的含量表现出一致的趋势,叶>根>枝>干.混交林乔木层各元素的积累量分别比纯林高47.97%~197.67%,凋落物层各元素贮量比纯林高85.40%~318.301%.混交林的年归还量、年存留量和年吸收量均大于马尾松纯林,且各元素循环系数大于马尾松纯林.马尾松林与阔叶树混交可以有效地提高群落生物量和营养元素循环的能力.     

Stability,transformations and stabilizing potential of an amorphous manganese oxide and its surface-modified form in contaminated soils

A surface-modified amorphous manganese oxide (SM-AMO) was prepared to increase the stability of a previously studied promising stabilizing agent and to compare its immobilizing efficiency with respect to contaminating metals with the original material. To synthesize the SM-AMO, the AMO surface was synthetically covered with a coating of MnCO₃ because newly formed rhodochrosite precipitates were previously found to increase the stability of AMO particles in soils. A preliminary experiment evaluating the long-term stability of both materials in pure water suggested higher stability for the SM-AMO particles, showing a smaller release of Mn compared to the original AMO. An adsorption kinetics study focused on As, Cd, Pb and Zn showed lower adsorption rates and adsorption capacity for Zn, probably as a result of partial surface passivation. In comparison to these results for simple controlled systems, different effects were recorded when the two materials were applied to contaminated soils. When incubated in soil, a constantly lower mass loss was recorded in the case of SM-AMO. There were no significant differences in the release of Mn and DOC into the soil solution or in the stabilizing efficiency with regard to contaminating metal(loid)s between the original and surface-modified materials. Concerning the potential solid phase transformations in soil conditions, we observed a gradual equilibration between the surface composition of both materials. While the newly formed rhodochrosite precipitated on the AMO surface, the MnCO₃ coatings on SM-AMO gradually dissolved. Both amendments also effectively supported microbial activity, especially in the more contaminated soil sample. Thus, despite the smaller mass loss, the effectiveness of both materials is comparable in the long term.     

中条山—塔儿山成矿带C─Fe─Au矿床成矿系列及成矿模式

中条山—塔儿山成矿带属滨西太平洋成矿域华北断块金、银、铜、铅、锌、锰、铝土矿、金刚石成矿区中的３级成矿带，其中包括２个成矿系列、７个成矿亚系列和１１个矿床式。２个成矿系列具有成矿世代的“双层性”、成矿物质来源的二元性、成矿作用的三阶段和矿化带展布与地质构造单元的趋近性等一系列特征     

安徽姑山矿浆型铁矿床Fe同位素初步研究

文章报道了宁芜矿集区内姑山矿浆型铁矿床中的铁氧化物、辉石闪长玢岩和赋矿围岩的Fe同位素组成,其δ57Fe的总体分布范围为-0.05‰~0.79‰。结果显示,姑山铁矿床的铁氧化物赤铁矿和镜铁矿均比硅酸盐岩浆结晶产物(辉石闪长岩)富集重的Fe同位素,并且硅酸盐岩浆的Fe同位素组成比已报道的火山岩的平均Fe同位素组成更富集轻的Fe同位素,表明在岩浆不混溶的过程中Fe同位素发生了分馏,富铁熔体相对富集重的Fe同位素,而硅酸盐熔体相对富集轻的Fe同位素;相对于赋矿地层(黄马青组石英砂岩)和辉石闪长玢岩,赤铁矿和镜铁矿更富集重的Fe同位素,围岩地层和闪长岩岩体则富集轻的Fe同位素。因此,姑山铁矿床的铁质不大可能来自于地层或闪长玢岩岩体,而主要来源于深部岩浆房。     

重庆城口高燕锰矿床矿物解离度与工艺粒度研究

随着当前矿产资源日趋贫、细、杂,合理利用低品位和复杂多金属矿石是目前选矿工作的重要问题（吴荣庆, 2008）,只有通过对矿物原料或产物中元素或矿物的状态和性质的系统研究,阐明其行为规律,指导和配合矿物加工研究和生产,才能有针对性地选择选矿方法和工艺流程（贾木欣, 2007）,实现对矿物资源的综合利用（吕宪俊,2001）。而矿物工艺粒度、解离度对选矿发挥着不可缺少的重要作用。矿物解离是选矿的必要条件之一,矿物工艺粒度、磨矿粒度等因素对矿物解离度都有影响,这些因素致使解离度和工艺粒度之间关系复杂化（洪秉信,傅文章., 2012）。本文通过对重庆城口高燕锰矿床矿物解离度与工艺粒度的研究,从而探讨解离度与工艺粒度对选矿加工的影响。     

内蒙古东升庙和炭窑口多金属硫化物矿床铁同位素地球化学特征及其成矿指示意义

本文报道了内蒙古狼山成矿带内两个最大的铅锌多金属硫化物矿床——东升庙矿床和炭窑口矿床中黄铁矿、黄铜矿单矿物的铁同位素研究结果。东升庙矿床绢云石墨片岩中不规则状黄铁矿的铁同位素组成δ~(56)Fe_(-IRMM)值在+0.04‰~+1.11‰之间,呈现铁的重同位素富集,指示了海水中的铁以氧化态沉淀并在成岩期转化成黄铁矿的矿化过程。东升庙和炭窑口矿床富硫化物矿石中黄铁矿和黄铜矿的铁同位素组成δ~(56)Fe_(-IRMM)值的变化范围为-1.33‰~+0.08‰,具有热液成矿特征,指示金属成矿物质来源于热液流体。另外,绢云石墨片岩中脉状黄铁矿的铁同位素组成δ~(56)Fe_(-IRMM)值的变化范围为-0.39‰~-0.04‰,处于矿石黄铁矿和围岩不规则状黄铁矿之间,指示脉状黄铁矿是热液矿化的产物,并在成矿过程中混入了围岩中早先形成的富集铁的重同位素的黄铁矿。绢云石墨片岩中广泛发育的不规则状黄铁矿与赋存在绢云石墨片岩中的富硫化物矿体具有完全不同的铁同位素组成,指示热液活动对不规则状黄铁矿没有明显成矿物质贡献,因此同沉积热液活动成矿的可能性不大。结合赋存在白云石大理岩中硫化物矿体的顶、底部常见硅化的白云石大理岩角砾,本文提出后生矿化是东升庙多金属硫化物矿体的主要成矿方式。另外,东升庙矿床和炭窑口矿床的矿石硫化物具有相似的铁同位素组成特征,指示两者的成矿物质来源具有相似性。     

Phytoplankton life cycle transformations lead to species-specific effects on sediment processes in the Baltic Sea

In order to study the sediment response to different addition of organic matter, we added cultures of the dinoflagellates Scrippsiella hangoei and Woloszynskia halophila and the diatom Pauliella taeniata to aquaria containing natural sediment. The biomass added was 1550–3260 mg C m⁻², and in the control, no biomass was added (n=3). Oxygen profiles at the sediment–water interface and inorganic nutrients in the near bottom water were determined once a week. In the additions of P. taeniata and W. halophila the sediment quickly became anoxic, and subsequently there was a flux of >1 mmol PO₄³⁻ m⁻² d⁻¹ out of the sediment in these treatments. The majority of the released P came from P stored in the sediment and not from the organic phosphorus added. The result was very different for the S. hangoei addition. This species underwent a life cycle change to form temporary cysts. During this process there was a net uptake of nutrients. After the formation of cysts the concentration of inorganic nutrient was similar to that of the control. Cysts generally survive for long periods in the sediment (months to years) before germinating, but can also be permanently buried in the sediment. The novel idea presented here is that the phytoplankton composition may directly affect sediment processes such as oxygen consumption and phosphorus release, through species-specific life cycle changes and yields of resting stages produced prior to sedimentation. This can be an important aspect of nutrient cycling in eutrophic waters, like the Baltic Sea, where there is large year-to-year difference in the amount of resting stages settling at the sea floor, mainly due to differences in abundance of diatoms and dinoflagellates during the spring bloom. If yields of resting stages change, e.g. due to changes in the phytoplankton community, it may lead to alterations in the biogeochemical cycling of nutrients.     

Nitrate in groundwater and N circulation in eastern Botswana

Nitrate pollution due to deep leaching from pit latrines has caused water supply wells in eastern Botswana to exceed health limits concerning nitrate. It was deduced from the estimated intake of salt and protein by the population that, as an average, about 10 percent of the human nitrogen excretion is leached to the groundwater. This fraction was also found in southern India, where on-the-ground excretion is customary. The nitrogen circulation in general in the savanna ecosystem is not appreciably affected in spite of a large livestock density. Overall nitrate leaching is in the order of 1.5 kg N/ha/y, similar to that in another semiarid area in southern India. However, in India, there seems to be a more diffuse areal leaching from agriculture as well as from villages.Measures to minimize the nitrate leaching could be to plant deep-rooted trees adjacent to pit latrines or to use latrines that separate the urine from the faces for a more near-surface infiltration facilitating plant uptake. Measures to minimize leaching will also lessen the rick for bacterial pollution of the groundwater.