云南会泽铅锌矿床地质特征及找矿方法模式

在矿床地质特征研究的基础上 ,着重讨论了银及分散元素的分布规律 ,总结出进行成矿预测的主要找矿标志及“重点解剖→点面结合→综合评价→工程验证”的找矿模式 ,提出了矿区重点找矿靶区 ,部分已被验证工程证实     

用改进的灰色识别法评价地表水环境质量——以北京石景山区莲花河新开渠为案例

简要论述了利用改进的灰色识别法评价地表水环境质量的计算原理、方法和步骤。改进的灰色识别法以灰色关联法为基础,针对运用灰色关联法对水环境质量进行评价中存在的问题,引入关联离散度和隶属度算法加以改进,并将水环境质量标准等级与相应的隶属度加权平均求得精确水质类别,进一步提高了分辨率和实用性。以北京市石景山区莲花河新开渠为案例,对地表水环境质量进行评价,确定其水质等级以及变化趋势,为水环境保护规划提供科学依据。结果表明:改进的灰色识别法可比性强,分辨率高,具有较高的实用价值。     

运用涂铁砂粒进行分散式饮水除砷的效果

采用铁盐处理普通河砂研制成涂铁砂粒(IOCS),通过静态和动态吸附试验观察其分散式饮水除砷效果,并选取地砷病现场进行了验证.结果表明,IOCS性质较为稳定,扫描电镜下可见铁氧化物呈片状分散的覆盖在砂粒表层;IOCS无需活化处理,其对砷的最大吸附发生在30min～60min;pH5～9时,五价砷的去除率随着pH值的升高而下降,三价砷的去除率变化不明显.IOCS对砷的吸附符合朗格缪尔(Langmuir)吸附方程;5次滤柱循环中,75g(50ml)的IOCS分别处理含砷1.0mg·L^-1的水样408～426床(三价砷),390～412床(五价砷),用0.2 mol·L^-1NaOH进行再生处理,砷回收率均在94%以上.充填IOCS 3.0kg的家庭用模拟装置处理含1.0mg·L^-1的五价砷209L和198L,三价砷196L和185L,并在现场实验期间,连续处理含砷0.202～1.733mg·L^-1的水样200L,对水质亦无不良影响.无论是经济上还是技术上,IOCS均是适合于分散式饮水除砷的一种新型除砷剂.     

Reverse quantitative structure-activity relationship for modelling the sorption of esfenvalerate to dissolved organic matter. A multivariate approach

The sorption of the pyrethroid, esfenvalerate, to the dissolved and/or dispersed fraction of eight different natural humic compounds has been investigated. The dissolved organic matters (DOMs) included in this study originate from ground water, soil pore water, and surface waters. Sorption was modelled at DOM concentration levels where equilibrium partitioning of esfenvalerate between DOM and the aqueous bulk phase prevails. The inherent characteristics of the eight different humic materials, quantified in the preceding paper by Thomsen et al. (2002, this issue (PII: S0045-6535(02)00335-1)), have been used as explanatory variables for modelling this equilibrium partitioning. Using a reverse QSAR approach based on by projection-into-latent-structure regression (PLS-R) inherent sorbent properties determining for the sorption affinity of esfenvalerate to DOM were analysed. For all humic substances a decrease in the DOM-normalised equilibrium-partitioning coefficient, K_DOM, with increasing concentration of DOM was observed. Significant variations in K_DOM values, as function of the inherent characteristics of the individual humic substances, were found at DOM concentrations of 75 and 100 ppm, respectively. The latter is a strong indication of variations in sorption mechanisms of esfenvalerate to DOM of varying inherent properties. Groupings in the principal property space quantifying DOMs may indicate that separate models are needed for quantifying the equilibrium partitioning to different classes of DOM.