几种常见震积岩相标志在模拟实验中的识别

震积岩相标志是识别震积岩的最有效依据。在对震浊积岩形成过程的水槽模拟实验中,发现了同沉积断裂、微褶皱纹理、液化砂岩脉、液化均一层、同沉积变形构造、震浊积岩等典型的软沉积物震积岩相标志,他们形成于地震作用的不同阶段,有规律的分布在三角洲—震浊积岩体系之中。同时,模拟实验中也发现了一些与震积岩相标志易混淆的其他成因相标志,因此在分析过程中应该充分考虑各种相标志的组合特征、与沉积环境的配置关系以及区域的构造背景等。依据模拟实验得出的震积岩相标志分布模式,通过相标志类型和组合特征分析,可进行震浊积体发育区带预测,指导断陷盆地隐蔽油气藏勘探。     

万泉寺银金矿成矿作用分析

万泉寺银金矿主要产于侏罗系白旗组二段地层中。其成矿作用主要为深部成矿物质随岩浆发生反重力迁移,最终通过较大断裂上升并于较大构造带中富集成矿。本文通过对该矿区成矿特征的阐述得出几点找矿标志,以便于对同类矿床的勘查提供参考。     

黑河地区金矿开发的环境影响研究

黑河地区是我国重要的矿产资源集中地,辖区矿产资源非常丰富,采取相应的措施有效做好黑河辖区矿产资源的可持续开采,对国家及黑河地区的经济社会发展具有非常重要的意义。文章重点分析了黑河地区的金矿赋存条件以及当前金矿的开发利用现状,明确了在金矿开发过程中存在的诸多环境影响问题,提出了黑河地区金矿开发开采过程中的环境指标评价体系。     

南海西北部陆架区沿岸流和上升流对中华哲水蚤分布的影响

中华哲水蚤(Calanus sinicus)是广泛分布于西北太平洋大陆架水域的浮游桡足类,在海洋生态系统的物质循环和能量流动中具有重要作用。根据2006年7月至2007年10月4个季节使用网目孔径为0.505mm的浮游生物网采集的样品,分析了南海西北部陆架区中华哲水蚤的水平、季节和昼夜垂直分布以及与季风、海流和温度的关系。中华哲水蚤丰度季节变化显著,整个调查海域春季的平均达(22.30±77.78)个/m3,夏季的降低,平均为(13.74±45.10)个/m3,秋季消失,冬季调查期间仍未出现。中华哲水蚤的区域分布差异十分显著,将调查海域划分为粤西近海、琼东近海、粤西-琼东外海三个亚区,在粤西近海亚区春、夏季中华哲水蚤的平均丰度分别为(115.63±145.93),(68.12±84.00)个/m3,远高于另外两个亚区。夏季琼东沿岸上升流区的中华哲水蚤没有昼夜垂直移动行为,呈底层分布,以躲避表层高温的伤害。南海西北部陆架区是中华哲水蚤的季节分布区,冬春季东北季风期间由广东沿岸流从东海沿岸携带而来,出现的时间从北往南逐渐推迟;夏季西南季风期间雷州半岛东部近海的冷涡和琼东沿岸上升流区成为中华哲水蚤度夏的避难所;秋季季风转换时期上升流减弱或消失,中华哲水蚤因耐受不了高温(>27℃)死亡而消失。因此,中华哲水蚤对东北季风时期的沿岸流和西南季风时期的上升流均具有良好的指示作用。     

黑潮及相邻海域表层砂壳纤毛虫分布模式:以夏季黄海、东海至西太平洋断面为例

2019年夏季对沿黄、东海至西太平洋跨越黑潮一个断面(122°E～145°E)的表层砂壳纤毛虫群落进行调查,研究了黑潮中砂壳纤毛虫与相邻水体的差异.根据水文环境及各站位所处的空间位置,我们将研究区域划分为大洋边缘区域、黑潮区域和大洋区域.各站位砂壳纤毛虫的丰度范围为3.95～31.94 ind·L–1,种丰富度范围为6...     

潍北平原土壤盐渍化现状及成因分析

通过环境地质调查及易溶盐测试,根据相关标准确定了潍北平原土壤盐渍化程度,并从地层、气象、地貌、水文地质、卤水开采等方面系统的分析了潍北土壤盐渍化形成原因,为当地土壤盐渍化防治提供了参考依据。     

基于粗糙集的BP神经网络在震例中的应用研究

采用《中国震例》作为数据源,通过初步整理分析和预处理,构建了较完备的震例研究样本集。尝试将粗糙集与BP神经网络相结合的方法引入到震例研究中,用基于粗糙集的属性约简算法从众多复杂的地震异常指标中筛选出对最终分类起决定作用的核心异常作为输入,震级作为输出,构建了泛化能力强的BP神经网络模型来模拟异常与地震之间的不确定关系。仿真测试结果表明:地震震级预测精度误差基本控制在-0.5～0.5级之间。     

Surveillance of Invasive Bacterial Pathogens and Human Enteric Viruses in Wastewater Final Effluents and Receiving Water Bodies – a Case Study from Durban,South Africa

The physico‐chemical characteristics and microbial composition of the final effluents of two municipal wastewater treatment plants in South Africa were assessed between July and September 2009. The impact of the treated final effluents on the receiving water bodies was also evaluated. The temperature across all sampling points ranged between 14 and 22°C, while pH varied from 6.9 to 7.6. High levels of turbidity, chemical oxygen demand (COD), ammonia, nitrate, nitrite and orthophosphate (PO₄) were observed in many cases. Turbidity of the samples was in the range of 2.2–288.6 NTU. The concentrations (mg/L) of other physico‐chemical parameters are as follows: COD (9.33–289); ammonia (0.000340–45.4); nitrate (0.062–539); nitrite (0.021–22.6); PO₄ (5.3–33.2). The microbial quality of the effluents discharged from the plants did not comply with the limits set by the South African guidelines with respect to pathogens such as Salmonella, Shigella, Escherichia coli, total coliform, faecal coliform, enterococci, faecal streptococci, and viral particles for effluents intended for discharge into receiving watersheds. This study revealed an undesirable impact on the physico‐chemical and microbial qualities of the receiving water bodies as a result of the discharge of inadequately treated effluents from the wastewater treatment facilities. This poses a health risk to several rural communities which rely on the receiving water bodies primarily as their sources of domestic water and recreational purposes. There is therefore a need for the intervention of appropriate regulatory agencies in South Africa to ensure compliance of treatment facilities with wastewater effluent quality standards.     

内蒙古孟恩陶勒盖银铅锌矿床地质特征及找矿标志

孟恩陶勒盖大型银铅锌矿产于晚二叠世花岗岩杂岩体中心部位,矿床的主要容矿构造为一组沿东西向或近东西向展布向东收敛的脆性断裂带.成矿作用大致经历了4个阶段,形成了44条脉状矿体,按容矿构造分布划分为上、中、下3个矿脉群,其中主矿体9条,较大分支矿体9条,主矿体上下盘小矿体26条.矿床自下至上,具锌矿石-银铅锌矿石-银铅矿石的明显分带性.工业矿物主要为闪锌矿、方铅矿、深红银矿、黑硫银锡矿、自然银,主要有益组分为锌、铅、银,主要伴生有益组分有铟、镉、镓、铜、锡、金.矿床成因初步认为是裂隙充填脉状银铅锌多金属中温热液型,找矿标志明显.     

New Zealand estuary benthic health indicators summarised nationally and by estuary type

ABSTRACT

Ecological data are often collected at small geographic scales. However, analysing data collectively over wider scales can reveal results and patterns not shown in the smaller-scale data. We summarised data for intertidal benthic ecological (physico-chemical and biological) health indicators from New Zealand estuaries and compared the results against thresholds above which ecological impacts are expected to occur. Values for the sediment physico-chemical indicators mud and nutrients (nitrogen and phosphorus collectively) were above thresholds for at least 50% and at 31% of sites measured respectively. Sediment organic content and metal concentrations were generally low, with only maximum values exceeding the thresholds. Scores for biological indicators were within (or better than) the moderate health category for either at least 50%, or at least 75%, of sites. When compared across estuary types (based on a geomorphic classification system) we found statistically significant differences for thirteen of the sixteen indicators. Differences (among mean values) for highly significant results were relatively large compared to the range of values observed nationally for those indicators. However, the differences, except those for mud, were smaller than their respective ecological health threshold values. Our summary provides a reference for future comparisons of estuary indicators nationally and across estuary types.