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11.
Dust samples collected from the Beijing metropolitan area (China) were evaluated to determine the distribution and the concentration of platinum group elements (PGEs). The dust particles that were smaller than 100 mesh size fraction (150 μm) were analyzed after aqua regia digestion. Concentrations ofPt, Rh, and Pd were found to be between 3.96 and 356.3 ng/g, 2.76 and 97.11 ng/g, and 0.1 and 124.9 ng/g, respectively, in the urban areas of Beijing, whereas for the background samples collected from the suburbs of Beijing, the concentrations of Pt, Pd, and Rh were very low and ranged from 0.1 to 0.9 ng/g, 0.5 to 1.4 ng/g, and 0.8 to 2.2 rig/g, respectively. The distributions of PGEs in road dust were an accurate reflection of the levels of pollution and were found to match with the local traffic conditions. A strong positive correlation was established among all the dements found in road dust. This suggests that emissions of abraded fragments from vehicle exhausts may be the source of the high concentration of Pt, Rh, and Pd in road dust along the main roads of Beijing.  相似文献   
12.
A Pt/WO3/TiO2 catalyst for propane oxidation was prepared by a stepwise wet impregnation method, and was aged at 800℃ for 5 hr. Compared to the sulfate-derived titania supported catalyst, the introduction of tungsten oxide as stable Bronsted acid sites led to the formation of more metallic platinum active sites at the Pt/WO3 interface. The dissociation of surface intermediates for propane oxidation was promoted on the WO3-modified catalyst. This, as well as the inhibition effects of tungsten oxide on the sintering of anatase and the phase transformation to rutile, resulting in a high activity and thermal stability for the Pt/WO3/TiO2 catalyst.  相似文献   
13.
Testing the mutagenic activity of environmental pollutants has become an important area of modern environmental science and prophylactic medicine. The most suitable method for short‐term mutagenicity testing on man, at present, are chromosome studies on somatic cells of exposed individuals. Mutation types analyzed by such studies are of high practical relevance as indicator system of genetic damage induced in man under in vivo conditions. A rather large series of such studies has been dedicated to the action of heavy metals on individuals contacted with these metals under therapeutic, ecological or occupational conditions or by intoxication. Lead, cadmium, chromium, nickel, mercury, zinc and other metals as well as their compounds have been under study. Analyses of that kind, of course, are hampered by difficulties with the distinct estimation of the actual load as well as unclear conditions of exposition, e.g. simultaneous exposition to different metals.

Results obtained till now arouse some suspicion of a direct or indirect mutagenic activity in man by certain chromium and platinum compounds, arsenic, mercury, and combinations of lead with other heavy metals (cadmium, zinc, arsenic, antimony, etc.). Life style, above all smoking habits, well may act comutagenic. In most cases, however, mutagenic activity of metals and metal compounds apparently is clearly superposed by their toxic activity. In specific cases, chromosome studies also may contribute to discover sources of ecological exposition and to monitor occupational load by heavy metals.  相似文献   
14.
铂族金属在地壳中储量稀少。随着汽车销量的增加及汽车尾气排放标准的提高,铂族金属的用量增长迅速。简要介绍了从废旧汽车尾气净化触媒中回收铂族金属的工艺流程及方法,随着研发技术的深入,铂族金属的回收利用率将大幅提升。  相似文献   
15.
上海市不同类型道路灰尘铂族元素(PGEs)空间分布特征   总被引:1,自引:0,他引:1  
刘玉燕  刘敏  王玉杰 《生态环境》2010,19(10):2414-2418
车辆行驶特征对PGEs排放影响很大,而不同类型道路,其车辆行驶特征会有很大差别。基于此,对上海市5条不同类型的道路进行灰尘PGEs空间分布规律的探讨。灰尘样品用王水消解制样,ICP-MS测定。结果表明:道路灰尘Rh、Pd、Pt的平均含量在主干道为24.50、96.40、29.04 ng·g-1,次干道为23.18、76.92、37.21 ng·g-1,快速路为41.73、188.05、57.21 ng·g-1,郊区高速公路为13.35、63.34、18.01 ng·g-1,郊区公路为7.49、22.76、0.97 ng·g-1,除次干道Pt含量高于主干道外,5种类型道路的PGEs含量均表现为:快速路﹥主干道﹥次干道﹥郊区高速公路﹥郊区公路,郊区高速公路及郊区公路虽然车流量大,但PGEs含量并不高,车流中许多车辆因未安装VECs而不排放PGEs是主要原因。如以1.5-1.6 km道路(两端为路口)为长度单位,主干道、次干道及快速路灰尘PGEs的分布呈波浪型;郊区公路灰尘PGEs的分布呈半圆弧型;郊区高速公路(仅有一端为收费口)灰尘PGEs分布呈先高后低再趋于平稳的折线型,车辆行驶特征的差异是造成不同类型道路灰尘PGEs分布模式差异的主要原因。郊区高速公路及郊区公路的路口(或收费口),PGEs含量往往很高;而主干道、次干道及快速路的路口,PGEs含量不一定很高,频繁的怠速和加减速使得上述三种道路远离路口的地方也常出现怠速是主要原因。  相似文献   
16.
纳米铂微粒电极催化氧化有机污染物的研究   总被引:3,自引:0,他引:3  
采用电化学阴极还原-阳极氧化方法制备了纳米铂微粒电极.电极表面的微观结构表征表明,铂微粒在三维网状的氧化钛膜孔道中呈均匀、高度分散状态,且粒径细小,铂微粒充分裸露,使得纳米铂微粒电极活性点多,电催化性能高.采用循环伏安法研究了铂微粒电极对有机小分子代表性物质甲醇的电催化氧化行为.结果表明,在酸性、中性和碱性介质中纳米铂微粒电极对甲醇的电催化氧化性能均明显优于光滑铂片电极,甲醇在纳米铂微粒电极上产生的氧化电流密度比光滑铂片电极高100倍以上.2种铂电极催化氧化降解甲醇、苯酚和甲基橙3种有机物时,纳米铂微粒电极的平均氧化电流效率是光滑铂片电极的数倍,这进一步表明纳米铂微粒电极对有机污染物具有良好的催化氧化降解能力.  相似文献   
17.
北京市中心城区道路尘土中铂族元素的污染特征   总被引:1,自引:1,他引:1  
为研究北京市中心城区铂族元素(PGEs)的污染状况,于2009年12月采集了二环道路尘土样品.样品经王水消解和阳离子交换树脂分离纯化后,采用电感耦合等离子体质谱法(ICP-MS)测定了道路尘土中PGEs的含量.结果表明,二环道路尘土中,Pd的含量为17.40~458.75 ng.g-1(平均值为126.66 ng.g-1),Pt的含量为10.04~182.89 ng.g-1(平均值为65.25ng.g-1),Rh的含量为4.00~68.04 ng.g-1(平均值为22.67 ng.g-1).与国内外其它城市相比,Pt含量偏低,Pd和Rh含量处于中等水平.总体而言,近几年道路尘土中Pd含量有了较大幅度的升高.中心城区的PGEs平均含量从大到小的顺序为:西二环≈东二环>北二环>南二环,主要受机动车流量控制.不同粒径的道路尘土中PGEs含量不同,0.125~0.25 mm粒径范围内尘土中的PGEs含量最高,而粒径<0.063 mm的尘土中PGEs含量较低.采用粒径<0.063 mm尘土中的PGEs含量来评价整个道路尘土中的PGEs含量容易导致结果偏低,从而低估其在环境的污染水平.  相似文献   
18.
Titanium dioxide(TiO2) samples of different crystal forms were prepared by hydrolysis tetrbutyl titanate in various water to alkoxide ratios and sintering the hydrolysis product at different temperatures.The photocatalysts coated on hollow glass beads and loaded with platinum varying from 0.2% to 2.4% by weight.The photocatalytic degradation rate of sodium pentachlorophenolate (PCP-Na) depends on the preparing conditions such as:sintering temperatures,water to alkoxide ratios(R),platinum content and the size.The proper conditions of preparation photocatalysts are as follows:the ratio of tiO2:sodium silicate:hollow glass beads:platinum is 10:5:20:0.15(w/w),R is 100,sintering temperature is 650℃,and the size of hollow glass is 0.5-1mm.Under these conditions,the ratio between acatase and rutile of the photocatalyst is 2:1,and the photocatalytic activity is high.  相似文献   
19.
The potential accumulation of platinum group elements (PGE) in the environment from automobile catalysts is high in urban areas, with the major sinks being roadside soils. Therefore, this investigation presented the detailed study on characterized concentrations of Pt and Pd and their enrichment ratios in urban roadside soils in Xuzhou, China in March 2003. Data from 21 roadside topsoil samples analyzed by inductively coupled plasma-mass spectrometer (ICP-MS) illustrated that the medians of concentrations of Pt and Pd were 2.9 and 2.8 ng/g, respectively. Hierarchical clustering analysis indicated that Pt and Pd were mainly from traffic emissions. Compared to unpolluted soils, computation of Pt and Pd enrichment ratios suggested that the Xuzhou roadside soils had average enrichment factors of 3.53 for Pt (in range of 1.22–5.73) and of 3.37 for Pd (in range of 1.35–4.46). Lower Pt/Pd ratios (in range of 0.35–2.86) in relation to similar studies in other countries were observed, which might be due to the different Pt/Pd ratios in Chinese automobile catalytic converters. Moreover, fine fraction (<250 μm) contained higher concentrations of Pt and Pd compared to the coarse fraction (250–500 μmm).  相似文献   
20.
生物法回收贵金属铂纳米颗粒及其机制   总被引:1,自引:1,他引:0  
商儒  朱能武  康乃馨  石超宏 《环境科学》2016,37(7):2799-2806
利用自行分离的粪肠球菌Z5(Enterococcus faecalis Z5)菌株(保藏号CCTCC M2012445)回收贵金属铂,探讨了其在外源电子供体条件下以纳米颗粒形式回收溶液中化合态铂的可能性,研究了铂初始浓度、生物量、温度以及p H值对回收过程的影响,探讨了粪肠球菌Z5回收铂纳米颗粒过程的可能机制.结果表明,粪肠球菌Z5菌株可以回收铂纳米颗粒,回收过程主要包括生物吸附和生物还原.铂初始浓度为286.46 mg·L~(-1)、生物量为3.2 g·L~(-1)、温度50℃以及p H值为6时为其最佳回收条件.X射线衍射(XRD)和透射电镜(TEM)分析表明,回收产物为5 nm左右粒径的铂纳米颗粒,主要分布于细胞周质.X射线电子能谱(XPS)分析显示,Pt(Ⅳ)首先被还原为Pt(Ⅱ),然后被还原为Pt(0),且从Pt(Ⅱ)还原成Pt(0)为限制步骤,傅里叶红外(FTIR)分析显示菌体表面的羟基和酰胺基官能团可能在回收过程中起作用.  相似文献   
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