青岛地区大气气溶胶中微量金属的时空分布

于 2 0 0 1年 4月— 2 0 0 2年 5月在青岛近海三个采样点采集了 1 0 0多个大气气溶胶样品 ,用ICP AES测定了Al,Fe ,Mn ,Cu ,Pb和Zn的浓度 ,讨论了这几种元素的时空分布特征及其来源 .结果表明 ,六种元素浓度的时空分布特征为 :沧口 >八关山 >仰口 ,TSP(总体悬浮颗粒物 )与Al,Fe ,Mn的浓度呈明显的季节变化 :春季 >冬季 >秋季 >夏季 ,而Cu ,Pb ,Zn的季节变化比较复杂 .六种元素中Al,Fe,Mn主要由自然过程输入 ,而Cu ,Pb ,Zn主要是人为来源 .     

山东省主要果园土壤中Cu、Zn的形态、含量及分布

对我国山东省主要果园土壤中的Cu、Zn元素的形态、含量及分布进行了研究。结果表明 :果园土壤中Cu、Zn元素的全量高于一般粮田土壤。在不同土壤类型中 ,形态分布各具特点 ,Cu元素在棕壤和褐土中的形态分布趋势一致 ,为矿物态 >有机态 >沉淀态 >交换态 ,在潮土和砂姜黑土中一致 ,为矿物态 >沉淀态 >有机态 >交换态 ;而Zn元素在这 4种土壤中的分布趋势相同 ,均为矿物态 >沉淀态 >有机态 >交换态。土壤中交换态的Cu、Zn含量随土壤pH值的增大而减小。Cu、Zn某些形态的含量与土壤中全量间有一定的相关性 ,其中沉淀态Cu与总Cu的关系较为紧密 ,2者呈极显著相关 ;矿物态Zn与总Zn也呈极显著相关。     

有机酸对砖红壤的溶解及固定态磷素的活化

选择柠檬酸、草酸、酒石酸和苹果酸4种土壤中常见有机酸为研究对象,研究了它们与砖红壤反应后,Fe、Al的溶出特征以及P的释放规律,并对上述反应的机制进行了探讨.结果表明,草酸、酒石酸和苹果酸3种有机酸与土壤反应24h后,溶液中总Fe浓度随反应体系pH值升高而降低,但柠檬酸与土壤反应24h后,溶液中总Fe浓度则随反应体系pH值升高而增加.4种有机酸溶出土壤Fe的能力按草酸柠檬酸酒石酸苹果酸的顺序下降,溶出机制主要是络合溶解和还原溶解.溶液中Al的溶出量在4种有机酸-土壤体系中均随体系pH值升高而降低,且按草酸柠檬酸≈酒石酸苹果酸的顺序下降,溶出机制主要是质子溶解和络合溶解.有机酸对固定态磷素有明显活化效应,在草酸、酒石酸和苹果酸3种有机酸-土壤体系中,溶液中P浓度均随体系pH值升高而降低,但在柠檬酸-土壤体系中,则随体系pH值升高而增加.溶液中Al/P物质的量之比要远大于Fe/P物质的量之比,这表明土壤中P主要结合在铁氧化物表面,其活化与铁氧化物的溶解过程关系密切.此外,Al的存在对草酸活化固定态P有抑制作用。     

基于两种样品前处理方法对比研究小冬克玛底冰川雪坑中痕量元素

通过对唐古拉山小冬克玛底冰川雪坑中非季风季节沉积的雪样分别进行酸化处理和消解处理后,利用高分辨扇形磁场等离子体质谱仪(ICP-SFMS)测试了样品中19种痕量元素(Ba、U、Sr、Rb、Tl、Mo、Cs、Pb、Sb、V、Cr、Mn、Fe、Co、Al、Cu、Ti、Li、As)的酸化浓度和总浓度.研究结果表明,痕量元素浓度的变化范围较大,元素Al的最大/最小浓度比为326(酸化浓度)和465(总浓度),元素Pb相应比值为27和48.雪冰中痕量元素的总浓度一般大于该元素的酸化浓度,其中,元素Pb、Fe、Sb、Ba、Al、Ti的酸化浓度占总浓度的平均比值分别为91%、76%、60%、52%、33%和21%.一般地,样品中不溶微粒含量越大,酸化浓度占总浓度的比值越小;不溶微粒含量越小,则相反.对痕量元素的富集系数(EF)分析表明,各元素总浓度EF均值小于酸化浓度EF均值,揭示了用酸化浓度计算EF存在对痕量元素人为来源影响的高估.人类排放是小冬克玛底冰川中痕量元素的来源之一,对于元素Mo和Sb,人类排放估计是主要来源.利用后向轨迹模型模拟出小冬克玛底冰川雪冰中痕量元素在非季风季节主要来源于青藏高原西部及中亚中东地区.     

大气PM_（2.5）中重金属的化学形态分布

运用多级连续提取法,对广州市不同季节不同采样高度大气PM2.5中重金属的化学形态和生物有效性进行分析。研究表明,PM2.5中各重金属元素之间的化学形态分布差异较大,Zn、Cd、As、Mn主要分布在F1（可溶态与可交换态）和F2（碳酸盐态、可氧化态与可还原态）,绝大部分的Pb以F2存在,Ni和Mo主要分布在F1和F3（有机质、氧化物与硫化物结合态）,Cu主要以F2和F3存在,Cr主要分布在F3和F4（残渣态）,Co则4种形态平均分布。采样高度对重金属的化学形态分布影响不大,同一采样期内楼顶与地面样品中同一元素的化学形态分布结果比较一致。两个采样季节重金属的形态百分比存在不同程度的变化,2007年春重金属的不稳定态（F1）比例比2006年秋普遍增加,次稳定态（F2、F3）比例减少。在10种重金属中,Cd、Zn、Pb和As的生物有效性系数高（〉0.7）,属于生物可利用性元素,在环境中的活动性要明显高于其它元素;Mn、Cu、Mo、Co、Ni和Cr元素的生物有效性系数值在0.2～0.6之间,属于潜在生物有效性元素,在环境中比较稳定。     

大气PM_(2.5)中重金属的化学形态分布

运用多级连续提取法,对广州市不同季节不同采样高度大气PM2.5中重金属的化学形态和生物有效性进行分析。研究表明,PM2.5中各重金属元素之间的化学形态分布差异较大,Zn、Cd、As、Mn主要分布在F1(可溶态与可交换态)和F2(碳酸盐态、可氧化态与可还原态),绝大部分的Pb以F2存在,Ni和Mo主要分布在F1和F3(有机质、氧化物与硫化物结合态),Cu主要以F2和F3存在,Cr主要分布在F3和F4(残渣态),Co则4种形态平均分布。采样高度对重金属的化学形态分布影响不大,同一采样期内楼顶与地面样品中同一元素的化学形态分布结果比较一致。两个采样季节重金属的形态百分比存在不同程度的变化,2007年春重金属的不稳定态(F1)比例比2006年秋普遍增加,次稳定态(F2、F3)比例减少。在10种重金属中,Cd、Zn、Pb和As的生物有效性系数高(>0.7),属于生物可利用性元素,在环境中的活动性要明显高于其它元素;Mn、Cu、Mo、Co、Ni和Cr元素的生物有效性系数值在0.2～0.6之间,属于潜在生物有效性元素,在环境中比较稳定。     

大气PM2.5中重金属的化学形态分布

运用多级连续提取法,对广州市不同季节不同采样高度大气PM2.5中重金属的化学形态和生物有效性进行分析。研究表明,PM2.5中各重金属元素之间的化学形态分布差异较大,Zn、Cd、As、Mn主要分布在F1(可溶态与可交换态)和F2(碳酸盐态、可氧化态与可还原态),绝大部分的Pb以F2存在,Ni和Mo主要分布在F1和F3(有机质、氧化物与硫化物结合态),Cu主要以F2和F3存在,Cr主要分布在F3和F4(残渣态),Co则4种形态平均分布。采样高度对重金属的化学形态分布影响不大,同一采样期内楼顶与地面样品中同一元素的化学形态分布结果比较一致。两个采样季节重金属的形态百分比存在不同程度的变化,2007年春重金属的不稳定态(F1)比例比2006年秋普遍增加,次稳定态(F2、F3)比例减少。在10种重金属中,Cd、Zn、Pb和As的生物有效性系数高(>0.7),属于生物可利用性元素,在环境中的活动性要明显高于其它元素;Mn、Cu、Mo、Co、Ni和Cr元素的生物有效性系数值在0.2～0.6之间,属于潜在生物有效性元素,在环境中比较稳定。     

厦门市大气降尘中重金属形态分布及生物有效性

采集了2012年11月至2013年1月期间厦门市大气降尘样品,用改进的BCR四步连续提取法分析了12种重金属元素(Ba、Ti、Co、Cr、Cu、Fe、Mn、Zn、Ni、Pb、Sr、V)的含量、赋存形态和生物有效性.结果显示,重金属元素四态含量之和均值(mg·kg~(-1))顺序为:Fe(43733)Zn(4495)Ti(2728)Ba(747)Mn(723)Cu(444.4)Sr(176)Cr(171)Pb(160)Ni(40.4)V(27.6)Co(11.2);Zn和Cu含量分别为我国土壤环境质量标准第二类标准限值(250和100 mg·kg~(-1))的18倍和4.4倍;除Fe、Ti、Ba、Cr和V外,大气降尘中其他元素生物有效态含量占有相当的比例(32.2%—88.6%).Zn、Sr主要以弱酸溶态存在,Pb主要以可还原态存在,Cu主要以可氧化态存在,其余元素主要以残渣态存在.大气降尘中重金属的平均生物有效性系数顺序为:Sr(0.87)Zn(0.85)Cu(0.80)Pb(0.67)Mn(0.50)Co(0.47)Ni(0.39)Ba(0.19)≈Cr(0.19)V(0.12)Fe(0.08)Ti(0.01),Ti、Fe、V、Cr和Ba为生物不可利用元素,Ni、Co、Mn和Pb为潜在生物可利用元素,Cu、Zn和Sr为生物可利用元素.     

北京地区大气颗粒物与元素浓度的概率分布

本文根据1983年从东单、北辛安、怀柔定期观测的结果,对颗粒物及Al、Ca、Cu、Fe、K、Mg、Mn、Pb、S、Ti、Zn的浓度频数分布类型进行检验。结果表明,它们的分布类型在这三个地点有些差异,但是,大多数元素浓度呈对数正态(或偏态)分布。依据分布类型,计算了这三个地点的颗粒物及元素浓度的平均值。对呈正态分布,采用算术平均值。呈对数正态分布,用几何平均值,对数正态分布以外的偏态分布经正态化处理后计算平均值表示。     

不同处理方法对降水中污染元素来源评估的不确定性讨论——以西藏拉萨和纳木错为例

在降水元素测试中对降水样品的前处理通常有两种方法:样品直接酸化和过滤后酸化.不同的处理方法会得到不同的结果,并最终影响到对元素来源的解释.为明确这两种处理方法对降水中重金属元素来源评估的影响,本文选取青藏高原的典型城市拉萨市和典型的背景区纳木错,对采集的24个降水样品用上述两种方法进行处理,并对两组样品中的15种金属元素的含量和富集因子进行了对比.结果表明,两个研究点过滤后样品元素含量都显著低于未过滤样品的元素含量,其中拉萨未过滤降水样品中的常量元素Al和Fe的含量分别比过滤后样品中的含量高约50和20倍,表明降水中的Al和Fe主要以颗粒态存在.相应地,典型污染元素如Cu、Zn和Cd等在两种样品中的含量变化相对较小,表明这些元素在降水中主要以溶解态存在.同样地,纳木错降水样品中元素也存在类似的变化特征.由于上述原因,拉萨和纳木错过滤后的降水样品中大部分元素(如Ni、Zn和Cd)的富集因子值高于未过滤样品中的值.因此,对降水样品过滤会导致一些典型污染元素的富集因子值增高,进而高估人类活动对这些元素的贡献.所以,用未过滤的降水样品进行元素富集因子研究得到的结果会更接近实际情形.     

Chemical composition of plant silica phytoliths

Silica phytoliths are a subgroup of biogenic opal. Silica phytoliths are formed in many plant species and remain preserved in soil and sediments after plant decay. The chemical composition of fossil phytoliths may reveal ancient plant taxa, soil composition and climate. However, actually detailed knowledge on silica phytolith composition is scarce. Here we present result of instrumental neutron activation analysis of barley awns, stems and leaves, and barley phytoliths. The elements of interest were Na, Mg, Al, Si, Cl, K, Ca, Sc, Ti, V, Cr, Mn, Fe, Co, Zn, As, Br, Rb, Sb, Cs, Ba, La, Ce, Sm, Eu, Tb, Dy, Yb, Hf, Ta, W, Th, and U. We compared three phytolith extraction methods: dry ashing, acid digestion, and acid digestion followed by incineration. We found that sole acid digestion is inefficient to remove organic matter. By contrast both dry ashing and acid digestion followed by incineration are suitable for phytolith analysis. Comparison of phytoliths with their source plant material shows that phytoliths are enriched in terrigenous elements such as Al, Sc, Ti, V, Cs, Fe, rare earth elements, and depleted in the major inorganic constituents of plants such as K, Ca, Mg, Mn, Cl and Br.     

用核子微探针进行单个大气颗粒物的分析

本文对单个大气颗粒物进行了分析研究，用核子微探针对首钢地区单个大气颗粒物进行了扫描分析，用三维等高线法给出了各种元素在一群单个大气颗粒物中的二维分布。从一群单个大气颗粒物中各元素的二维分布可对首钢地区大气污染的特征及来源进行分析研究。     

Geochemistry of the barkinite liptobiolith (Late Permian) from the Jinshan Mine,Anhui Province,China

This paper discusses the geochemistry and mineralogy of the barkinite liptobiolith of the Late Permian age from the Jinshan Mine, Guangde County, Anhui Province, China. Samples were examined using inductively coupled plasma-mass spectroscopy, X-ray fluorescence, cold-vapor atomic absorption spectrometry, ion-selective electrode, sequential chemical extraction, scanning electron microscopy equipped with energy-dispersive X-ray, and optical microscopy. The coal is a medium-ash and high-sulfur resource. Minerals in the coal are composed of kaolinite, pyrite, calcite, and quartz. Pyrite and calcite are derived from seawater during peat accumulation. Quartz in the coal is of authigenic origin. Part of the kaolinite is from a land-source region, and part occurs as cell-fillings and is of authigenic origin. The results also indicate that the barkinite liptobiolith contains some toxic elements in high concentrations. Elements including Li, Be, Si, Sc, Ti, V, Cr, Fe, Ga, Se, Y, Zr, Mo, the rare earth elements (REEs), W, Hg, Tl, Pb, Th, and U in the coals are enriched in the barkinite liptobiolith. Results of sequential chemical extraction showed that Li, Sc, Ti, Cr, Y, Zr, REEs, and Th in the coal mainly occur as silicates, while Be and W are related to organic matter. Pyrite is the dominant source of S, Mo, Hg, Tl, and Pb. Gallium only occurs in silicate, and U and V occur both in organic and silicate associations.     

渭河流域关中段地表水重金属的污染特征与健康风险评价

由于重金属的毒理性及其对水生生态系统的重要影响,水生环境的重金属污染已成为全世界关注的问题.渭河是黄河的第一大支流,近年来随着沿岸社会经济的发展,渭河的水质受到严重的威胁,但是对渭河流域地表水重金属的污染状况缺乏全面评估.以渭河流域关中段为研究区域,采集了该流域35个地表水样品,检测了12种重金属元素(Cr、Mn、Fe...     

The chemistry and parent material of urban soils in Bristol (UK): implications for contaminated land assessment

An earlier survey of topsoil from parks and allotment in the city of Bristol (UK) revealed the presence of relatively high levels of “pseudo-total” Cd, As, Cu, Pb and Zn, with Cd and As exceeding present UK soil guidelines. This follow-up work aimed at (1) estimating geochemical thresholds for these elements based on “near-total” soil, bedrock and sediment heavy metals and (2) determining the genetic relationship between soil and bedrock using rare earth elements (REEs or lanthanides) as tracers. “Near-total” concentration of 34 elements (Al, Ca, Fe, K, Mg, Na, As, Ba, Cd, Cr, Cu, Li, Mn, Ni, P, Pb, Sc, Ti, V, Zn, Y and the rare earth elements Ce, Dy, Er, Eu, Gd, Ho, La, Lu, Nd, Pr, Sm, Tb, Yb) were obtained by ICP-MS and ICP-OES. The results show that the soil composition is largely controlled by the soil parent material, though extreme outliers are indicative of contamination at a few sites of parkland and allotments. Cumulative frequency plots show the presence of different data sets for which separate “background” values should be determined. The REE data provide evidence that weathering of the underlying sandstone was a determinant factor leading to the relatively high heavy metal enrichment found in soil samples and sediments. Reference to UK soil guidelines to decide on possible remediation measures could be very misleading due to the natural high background levels of some elements in the underlying bedrock. Before defining land as “contaminated”, a thorough geochemical investigation is required at local scale in order to produce a more realistic and correct environmental assessment.     

Elemental concentrations in Jamaican peat

The peat of the Negril Morass in Western Jamaica was sampled at depths down to 7 m in directions parallel and perpendicular to the seashore, and the samples were analysed for Al, As, B, Br, Ca, Ce, Cl, Co, Cr, Cs, Dy, Eu, Fe, Hf, I, La, Mg, Mn, Na, Sb, Sc, Sm, Sr, Ti, U and V by instrumental neutron activation analysis and by spectrophotometry. The peat is high in ash content, but the concentrations of most elements are below crustal abundances and therefore provide no evidence of nearby mineralisation. The elemental concentrations indicate that no particular environmental hazards are to expected from the use of this peat in electricity generation.     

Löwenzahn Taraxacum officinale Web. als (städtischer) Bioindikator

Investigations of the dandelion, Taraxacum officinale Web. in Poland, Romania and Germany showed that the species concentrates various elements dependent on the intensity of the pollutants. In this study, we followed up the question of whether T. officinale enriches pollutants by the atmospheric deposition on the leaves or via the soil. Therefore, samples from at least 10 plants and a soil sample at 57 sample sites were collected from a grid of 500 m × 500 m. In addition to the analysis of the total soil sample, the (mobile) ion pool of the soil (DIN V 19739) was analysed. The elements Al, As, Ba, Ca, Cd, Ce, Co, Cr, Cu, Fe, Ga, K, Mg, Mn, Mo, Na, Ni, Rb, Sr, Ti, Tl, V, and Zn were determined through the use of spectrometry with inductive coupled plasma (ICP-MS and ICP-OES). The results are compared with the element concentrations of washed and unwashed leaf samples in T. officinale. We could only find two direct correlations (Ti and Zn) between the element content, of the entire soil samples, but 14 correlations (As, Ba, Cd, Cu, Ga, K, Mn, Mo, Na, Ni, Rb, Ti, Tl und Zn) between the ion pool of the soil and the washed samples. The grid point data interpolation by ArcInfo showed a similar distribution pattern for the unwashed leaf elements Al, Ce, Fe, Ti and V (r≥0.75). The elements Al, Ce, Fe, Ti, and V are washed out at the same ratio. Thus, although the concentration of these elements were significantly reduced by the washing procedure, the correlations were not influenced. The admissibility of the grid point data interpolation for a distribution map of the town area was investigated, as well. It is shown that the element content varies with the land use (meadow, field, rural areas), the sampling point and the local pollutants. However, none of the discussed elements, Al, Ce, Fe, Ti, and V, is significantly influenced by the land use. The data allows one to make the conclusion that the elements of Al, Ce, Fe, Ti and V are dependent on the dry and wet deposition on the leaves of T. officinale. These elements are taken up not only by the roots, but also by the surface of the leaves. This is evident because there is no correlation between one of these elements in the leaves and the ion pool of the soil.     

Concentrations of various elements and inorganic ions in rice straw and ash

Various elements and inorganic ions in rice straw and ash samples were analyzed by using inductively coupled plasma atomic emission spectrometry (ICP‐AES) and ion chromatography (IC). Five major elements: Mg, Mn, Al, Ca, and Fe and eight minor and trace elements: Cr, Cu, Ti, Zn, La, Sr, Ba, and Hg were detected in these samples, at more than ppm‐level. In ash samples the trace elements such as Y, As, V, Se, and Sc were also identified. The concentrations of SO₄, PO₄, Cl, Na, and K ions in these samples were higher than those of other ions measured. These elements and inorganic ion concentrations were approximately one order of magnitude higher in the ash than in the straw samples. Gas chromatography/mass spectrometry (GC/MS) and library search showed the presence of fatty‐, carboxylic‐ and nicotinic acids, and their derivatives in small quantities in the straw samples.     

Pattern of distribution of selected trace elements in the marine brown alga,Sargassum filipendula Ag. from Sri Lanka

Baseline concentrations together with biological variations of 29 trace elements (Ag, As, Au, Ba, Br, Cd, Ce, Co, Cr, Cs, Eu, Fe, Hf, I, Mn, Mo, Ni, Pb, Rb, Sb, Sc, Se, Sm, Sr, Tb, Th, Yb, Zn and Zr) were investigated in the brown alga, Sargassum filipendula collected from the western coast of Sri Lanka. Several elements (Co, Cr, Fe, Hf, Ni, Sc, Se, Th, Zr and the rare earth elements) were found to be enriched in S. filipendula compared to NIES No. 9 Sargasso reference material. Concentration of strontium in S. filipendula was highest at all sites. Chemical abundance of the rare earth elements decreased approximately linearly with increasing atomic numbers. The pattern of elemental distribution appears to be due to the fact that S. filipendula seems capable of concentrating high levels of trace elements under conditions of their very low availability in sea water. Concentration factors for elements in S. filipendula lie in a higher range compared with those reported in the literaure for brown algae.     

外源稀土在土壤中的形态转化研究

研究了外源可溶性稀土进入土壤后的形态分布及形态转化的时间进程。外源稀土进入土壤（华北潮土）后迅速向各个形态转化,实验进行了６０ｄ,稀土形态在此期间的变化结果表明：交换态迅速下降;碳酸盐结合态的变化情况与交换态基本相同,只是下降的幅度较交换态小;铁锰氧化物结合态生微弱地上升,然后逐步下降;有机结合态则先稳定再逐步升高,外源稀土可在此态积累;残渣态在实验期内基本稳定,无明显变化。