海洋藻类--对付全球变暖的武器?

最近,由欧盟(则资助的研究项目(Parforce)研究人员发现了海洋藻类与气候变化之间的联系。项目研究人员发现,从海洋藻类及浮游生物释放的碘蒸汽,在海面上浓缩,形成对抗地球变暖的悬浮微粒。此悬浮微粒对地球气候变化及降     

滇西沘江流域水体中重金属元素的地球化学特征

通过测定流经兰坪金顸铅锌矿区的沘江水体中Pb、Zn、Cd、As的含量和底泥中重金属元素的化学形态的含量,分析了重金属元素的分布和化学形态的变化。结果表明,沘江水遭到了Cd污染,底泥已经成为重金属元素的蓄积库,以国家土壤环境质量标准（Ⅲ级）衡量,Pb、Zn、Cd和舡分别超标3．4倍、15．8倍、106倍和2．6倍。沘江水中重金属元素含量的峰值在矿山附近的下游,而底泥中重金属元素的峰值在矿山下游30-50km的地方,矿业活动、水流变缓、pH等水体环境条件的变化都能影响水和底泥中重金属元素的含量。底泥中的Pb以碳酸盐结合态为主,Zn和Cd以铁锰氧化物结合态为主,而As以残渣态为主。Pb、Cd、Zn三种元素的环境有效态含量比较高,对沘江流域生态环境具有潜在的巨大的危害。     

中国首例铁氧化物-铜-金-铀-稀土型矿床的厘定及其成矿演化

通过对拉拉矿床物共生组合、矿物生成顺序、矿石特征的研究，发现其矿石物以磁铁矿为主，铁和铜的硫化物次之，并含有大量稀土矿物和自然金。拉拉矿床至少经历了两期成矿作用：早期为区域变质成矿作用，晚期为热液成矿作用。早期形成Fe-REE-P矿化，晚期为Cu-Mo-Au-Co-(U)矿化。根据这些特征，首次指出该矿床属于铁氧化物-铜-金-铀-稀土型矿床，而不是以往所称的块状硫化物型铜矿。     

稀土复合氧化物加少量贵金属汽车尾气三效催化剂性能研究

研究了稀土、过渡元素复合氧化物加少量贵金属汽车尾气三效催化剂的性能，包括蜂窝状第一载体粉碎后制备样品的性能、整块蜂窝状催化剂经粉碎后实验室测定的三效活性与组装成反应器安装在长安奥拓车上的净化性能。     

大气杀手——酸雨

酸雨 ,顾名思义 ,就是大气中的硫氧化物、氮氧化物等溶于纯净的雨水中 ,使雨水具有弱酸性 ,即谓之酸雨。如果说 ,十多年前 ,酸雨还只是个别国家的局部性问题 ,那么随着各国矿物燃料消耗量的不断增加 ,排入大气中的二氧化碳、硫氧、氮氧化物等日渐增多 ,目前酸雨的危害已向全世界蔓延 ,并成为当代世界的重大环境问题之一。硫氧化物和氮氧化物来源于何处呢 ?一是自然来源。如火山喷发时 ,就有二氧化硫的喷出 ;沼泽、土壤、坑道等地的含硫物质 ,在厌气细菌的作用下 ,会以硫化氢的形式释放出来 ,经周围环境的氧化后 ,生成二氧化硫 ;沉积在海洋中…     

Water soluble components of PM10 Chongqing, China

The concentrations of water soluble ions (Na⁺, NH₄ ⁺, K⁺, Mg²⁺, Ca²⁺, NO₃ ^-, Cl^-, and SO ₄ ^2- ) in PM₁₀ samples collected on cellulose filters by a medium-volume cascade impactor were determined, which were obtained from three kinds of areas in Chongqing: industrial area (Jiulongpo district), commercial and residential area (Jiangbei district) and background area (Jinyun Mountain in the Beibei district). The results showed that except for the background site, the annual average values of PM₁₀ are 23% – 61% higher than the national air quality standard (GradeII) (0.1 mg/m³), even that the value of the control site is still 20% higher than American standard (0.05 mg/m³). This implied that serious pollution of fine particles occurred in Chongqing. Nine kinds of soluble ions in water of PM₁₀ were analyzed by ion chromatography (IC) and the annual average concentrations follow the order of [SO ₄ ^2- ] > [NO³ _-] > [Cl^-] > [F^-], and [Ca²⁺] > [NH₄ ⁺] > [K⁺] > [Na⁺] > [Mg²⁺]. Their values were different in these areas: the industrial area > the commercial and living area > the control area. As for NH_{4 +}, K⁺, Ca²⁺, NO₃ ^- and SO ₄ ^2- , their seasonal average concentrations show a similar variation trend: the values in spring and fall were higher than those in summer and winter. The seasonal average concentrations of [Cl^-], [F^-], [Na⁺] and [Mg²⁺] are much lower than those of other ions. However, the concentrations of [Na⁺] changed more greatly in different seasons than those of the other three ions. Correlation coefficients showed that the three areas have been polluted by coal smoke and dust to different extents, while some local resources of pollution should be taken into consideration as well.