湖南省铅锌金银多金属矿床地质特征与成矿规律

在对前人典型矿床研究的基础上,总结了湖南省铅锌金银多金属矿床的地质特征、成因类型及成矿规律,重点分析了13处铅锌金银多金属(铜、钨、锡等)矿床(体)的地质特征及成矿机制.湖南省铅锌金银多金属矿床包括接触交代型(夕卡岩型)、岩浆热液型(充填交代型及蚀变岩型)和浅成中-低温热液型(沉积热液再造型)3个三级(四级)成因类型....     

基于TOUGHREACT的成矿过程化学反应数值模拟——以虎头崖铅锌多金属矿床为例

虎头崖铅锌多金属矿床是青海省祁漫塔格成矿带中典型的矽卡岩型矿床。本文基于前人对该矿区地质特征、矿物学和地球化学特征等方面的研究成果，利用TOUGHREACT数值模拟软件，针对石英-晚期硫化物成矿阶段进行成矿过程化学反应数值模拟研究。通过建立地质概念模型和网格化物化参数的设置，在设置的时间步长内对多相流体流动和热对流传导、溶质运移以及地球化学反应过程进行模拟计算，研究了矿区内不同温压条件下成矿元素化学平衡浓度变化的总体趋势以及对方铅矿和闪锌矿矿物溶解沉淀情况的影响。结果表明：当温度从250℃降至155℃时，Pb²⁺的化学平衡浓度出现骤减；当温度从300℃降至100℃时，Zn²⁺的化学平衡浓度出现骤减；由于矿物的沉淀需要消耗大量相关的成矿元素，方铅矿和闪锌矿最佳成矿温度范围分别为155℃~250℃和100℃~300℃；不同温度和压力对成矿元素化学平衡浓度影响不同，温度是控制方铅矿和闪锌矿沉淀化学反应的核心因素，压力的影响较小。模拟结果与传统地质解译结果相对符合，证明了模拟的有效性。     

煤层气在煤储层中的扩散及其影响因素

煤层气在煤储层中的扩散是指从煤基质孔隙表面上解吸的煤层气运移到割理系统的主要过程。发生扩散的前提条件是气体浓度差的出现，衡量扩散能力大小的重要参数是扩散系数。前者为由解吸速度、解吸气量和煤层气产量、井孔压力降等因素控制的动态参数，而后者为主要受扩散物质性质、扩散介质特征、扩散系统的温度、压力和孔隙结构形态等因素影响的静态参数。煤层气在煤储层中的扩散量与煤层气浓度差和扩散系数呈正比关系。     

一次飞机积冰环境中的云微物理特征

2014年3月12日利用机载粒子探头(DMT)对我国宜昌及周边地区的非降水云系进行了探测时发现了少量的飞机积冰,本文分析了积冰云层中云微物理量的分布特征。垂直平均分布表明,CAS、CIP和PIP粒子数浓度分别大于300个·cm~(-3)、1个·cm~(-3)和10~(-5)个·cm~(-3),粒子中值直径最大值分别为3μm、89μm和1389μm。谱分布表明,3650m高度重力碰并和凇附过程使得CIP和PIP粒子谱较宽,3650m以下谱宽较窄,粒子以凝结增长为主,大粒子和冰晶粒子主要是由高层下落造成。平飞观测统计表明,3350m的CAS和CIP粒子平均数浓度均大于3650m的值,但PIP粒子数浓度、粒子平均和最大中值直径则相反。平飞时间变化表明,3350m高度CAS粒子数浓度和直径大致呈反相关,3650m大云滴和冰雪晶粒子的数浓度和中值直径随时间波动较大。     

内蒙古东部春季三类沙尘天气气溶胶散射系数及其与PM10、能见度相关性分析

利用内蒙古东胜、锡林浩特两站2004~2006年春季（3~5月）积分浊度计的观测资料,结合同期PM10质量浓度、大气能见度等资料,分析了背景、扬沙、沙尘暴、强沙尘暴等不同强度沙尘天气气溶胶散射系数的分布特征,讨论了不同强度沙尘天气过程中散射系数、PM10、能见度的日变化规律,以及不同强度沙尘天气过程中散射系数与PM10质量浓度、散射系数与能见度的相关关系。结果表明:散射系数能够很好地反映沙尘天气强度;随沙尘天气强度增强,散射系数日变化从双峰型向单峰型转变;沙尘天气强度较弱时,PM10与散射系数的日变化不相似,强沙尘暴过程中PM10与散射系数的日变化有一定的相似性;能见度与散射系数日变化趋势相反;散射系数与PM10质量浓度呈正相关性,沙尘天气越强,相关性越好,背景、扬沙、沙尘暴、强沙尘暴相关系数分别为0.201、0.809、0.898和0.953;散射系数与能见度有指数相关关系,随沙尘天气强度增强二者相关性逐渐增强,背景、扬沙、沙尘暴、强沙尘暴相关系数分别为-0.773、-0.870、-0.918和-0.940。     

桂林城区大气能见度与颗粒物浓度和气象因子关系研究

利用2015年1月至2017年6月桂林国家基本气象站能见度、相对湿度、气温、气压、降水等气象要素和PM₁₀、PM_2.5、PM_1.0颗粒物质量浓度资料,分析桂林城区大气能见度与颗粒物浓度和气象因子之间关系。结果表明：桂林城区大气能见度和PM₁₀、PM_2.5、PM_1.0呈对数关系,相关系数分别为-0.341、-0.461、-0.509,颗粒物对大气能见度影响在相对湿度为60%—70%时最为显著。在各气象因子中,大气能见度与风速的相关性最好,其次为相对湿度,与风速呈二次函数关系,与相对湿度呈幂指数关系,与温度相关性较小,与气压在秋冬季节呈正相关,相关系数冬季可达0.301,但在春、夏季节相关性不显著;利用颗粒物浓度和气象要素建立8种大气能见度非线性统计回归模型,比较后发现利用PM_1.0、风速、相对湿度、气温等因子建立的不同季节大气能见度拟合公式在实际检验中效果最优,能较好地模拟桂林地区大气能见度的变化。     

铁同位素的MC-ICP-MS测定方法与地质标准物质的铁同位素组成

详细报道了在低分辨和高分辨模式下运用MC-ICP-MS进行Fe同位素比值高精度测试的方法,对Fe同位素测定过程中谱峰干扰、基质效应、浓度效应、仪器测试的长期重现性等问题进行了评估,并对两种运行模式的测试结果进行了对比.在95%的可信度范围内,所建方法的外部精度优于0.5ε/ainu,达到国际同类实验室的先进水平,并且低分辨和高分辨两种模式下获得的Fe同位素测试结果是一致的.在此基础上对国家地质标准物质GBW07105(玄武岩)和GBW 07111(花岗闪长岩)进行了Fe同位素测定.相对于Fe同位素国际标样IRMM-014,GBW07105的Fe同位素成分为:ε57Fe=1.9±0.3(20),ε56Fe=1.3±0.2(2σ),ε57/56Fe=0.6±0.1(2σ);GBW 07111的Fe同位素成分为:ε57Fe=1.8±0.4(2σ),ε56Fe=1.2±0.2(2σ),ε57/56Fe=0.6±0.1(2σ).     

Vertical structures of PM10 and PM 2.5 and their dynamical character in low atmosphere in Beijing urban areas

The vertical structures and their dynamical character of PM2.5 and PM10 over Beijing urban areas are revealed using the 1 min mean continuous mass concentration data of PM2.5 and PM10 at 8, 100, and 320 m heights of the meteorological observation tower of 325 m at Institute of Atmospheric Physics, Chinese Academy of Sciences (IAP CAS tower hereafter) on 10―26 August, 2003, as well as the daily mean mass concentration data of PM2.5 and PM10 and the continuous data of CO and NO2 at 8, 100 (low layer), 200 (middle layer), and 320 m (high layer) heights, in combination with the same period meteorological field observation data of the meteorological tower. The vertical distributions of aerosols observed on IAP CAS tower in Beijing can be roughly divided into two patterns: gradually and rapidly decreasing patterns, I.e. The vertical distribution of aerosols in calm weather or on pollution day belongs to the gradually decreasing pattern, while one on clean day or weak cold air day belongs to the rapidly decreasing pattern. The vertical distributive characters of aerosols were closely related with the dynamical/thermal structure and turbulence character of the atmosphere boundary layer. On the clean day, the low layer PM2.5 and PM10 concentrations were close to those at 8 m height, while the concentrations rapidly decreased at the high layer, and their values were only one half of those at 8 m, especially, the concentration of PM2.5 dropped even more. On the clean day, there existed stronger turbulence below 150 m, aerosols were well mixed, but blocked by the more stronger inversion layer aloft, and meanwhile, at various heights, especially in the high layer, the horizontal wind speed was larger, resulting in the rapid decrease of aerosol concentration, I.e. Resulting in the obvious vertical difference of aerosol concentrations between the low and high layers. On the pollution day, the concentrations of PM2.5 and PM10 at the low, middle, and high layers dropped successively by, on average, about 10% for each layer in comparison with those at 8 m height. On pollution days, in company with the low wind speed, there existed two shallow inversion layers in the boundary layer, but aerosols might be, to some extent, mixed below the inversion layer, therefore, on the pollution day the concentrations of PM2.5 and PM10 dropped with height slowly; and the observational results also show that the concentrations at 320 m height were obviously high under SW and SE winds, but at other heights, the concentrations were not correlated with wind directions. The computational results of footprint analysis suggest that this was due to the fact that the 320 m height was impacted by the pollutants transfer of southerly flow from the southern peripheral heavier polluted areas, such as Baoding, and Shijiazhuang of Hebei Province, Tianjin, and Shandong Province, etc., while the low layer was only affected by Beijing's local pollution source. The computational results of power spectra and periods preliminarily reveal that under the condition of calm weather, the periods of PM10 concentration at various heights of the tower were on the order of minutes, while in cases of larger wind speed, the concentrations of PM2.5 and PM10 at 320 m height not only had the short periods of minute-order, but also the longer periods of hour order. Consistent with the conclusion previously drawn by Ding et al., that air pollutants at different heights and at different sites in Beijing had the character of "in-phase" variation, was also observed for the diurnal variation and mean diurnal variation of PM2.5 and PM10 at various heights of the tower in this experiment, again confirming the "in-phase" temporal/spatial distributive character of air pollutants in the urban canopy of Beijing. The gentle double-peak character of the mean diurnal variation of PM2.5 and PM10 was closely related with the evident/similar diurnal variation of turbulent momentum fluxes, sensible heat fluxes, and turbulent kinetic energy at various heights in the urban canopy. Besides, under the condition of calm weather, the concentration of PM2.5 and PM10 declined with height slowly, it was 90% of 8 m concentration at the low layer, a little lesser than 90% at the middle layer, and 80% at the high layer, respectively. Under the condition of weak cold air weather, the concentration remarkably dropped with height, it was 70% of 8 m concentration at the low layer, and 20%―30% at the middle and high layers, especially the concentration of PM2.5 was even lower.     

承德市臭氧污染气象条件预报方法研究

利用2014-2016年承德市环境监测站和气象站的数据,分析了气象条件对承德市O₃-8h浓度的影响,探讨了臭氧污染气象条件的预报方法。结果表明：4-7月是承德市O₃-8h浓度较高的月份,O₃浓度的日变化特征为午后浓度高而夜间浓度低;O₃污染的天气形势为500 hPa受高压脊和偏西气流影响,850 hPa有强暖平流和20℃以上的高温,地面受低压前部和高压后部之间的偏南气流影响;有利于O₃-8h出现高浓度的气象因子为日平均气温大于23℃、日最高气温大于28℃、日平均海平面气压995-1007 hPa、日平均水汽压18-28 hPa、偏南风大于1 m·s^-1。利用气象因子综合评分建立臭氧污染指数,与O₃-8h浓度的相关系数高达0.7553,说明臭氧污染指数能较好地预报臭氧污染天气。     

RegCM-Dust模式对东亚一次沙尘暴天气过程模拟的效果检验

为检验区域气候模式与沙尘模式耦合模式RegCM Dust的性能,以2006年东亚地区一次沙尘暴过程为例,将模拟结果与观测资料进行对比,以检验模式对沙尘天气过程的模拟能力。结果表明：模式对沙尘暴过程的地面风场特征模拟效果较好,总体上重现了大风区的分布;地面沙尘浓度和沙尘光学厚度模拟结果与观测分布总体吻合。模式虽然是区域气候模式与沙尘模式耦合模式,但由于其内核是建立在中尺度数值模式MM4基础上,因此对天气过程尤其是沙尘天气过程具备较好的把握能力,对于沙尘天气过程预测具有良好的应用前景。