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101.
烟台市是山东半岛蓝色经济区核心城市之一,通过对山东省烟台市生态地球化学资料的系统整理,研究土壤重金属污染现状与分布迁移规律,发现土壤主要污染因子是As、Cd、Hg、Cu、Pb、Zn等重金属元素污染,工矿三废排放是土壤重金属污染的主要原因;主要致污因子砷是环境中毒性最大的有害元素之一。土壤-苹果树体系中As迁移及形态转化规律为:植物根系吸收土壤中的砷,并在根部发生了AsⅤ→AsⅢ的还原作用,由植物的根部向上迁移过程中,AsⅢ的比例逐渐降低。砷在根系土-植物体系中的分布为:根系土>根>叶子>茎>苹果。 相似文献
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在特提斯喜马拉雅带东段哲古错中低温热液型锑-金矿床内首次发现了含金(砷)细粒高镁石英闪长岩,它们呈岩脉或岩枝状侵入于上三叠统—下侏罗统黑色页岩中。矿区内及外围有许多辉长岩脉及少量橄榄二辉岩小岩体产出。含金(砷)细粒高镁石英闪长岩主要为细粒结构,其次为斑状结构,具有与高镁埃达克岩相似的地球化学特征,表现为:SiO_2≥56%,高Al_2O_3(>15%)、高MgO(Mg~#值为48~59),高Cr(75×10~(-6)~130×10~(-6))、高Ni(54×10~(-6)~74×10~(-6)),富集LILE,亏损HREE及HFSE,(La/Yb)_N>12,Eu弱负异常(δEu=0.81~0.91),Sr含量较高且变化大(209.28×10~(-6)~685.14×10~(-6),平均381×10~(-6))、低Y和Yb,Y<16×10~(-6),Yb<1.7×10~(-6),具有平坦的HREE配分型式,(Ho/Yb)_N≈1,Sr/Y值较高且变化大(14.58~47.28,平均24)。Nd-Sr-Pb同位素组成特征为:高I_(Sr)(0.709726~0.711203),ε_(Nd)(t)弱负(-3.08~-1.15),Pb同位素组成变化幅度不大,~(206)Pb/~(204)Pb=18.638~18.672,~(207)Pb/~(204)Pb=15.694~15.702,~(208)Pb/~(204)Pb=38.983~39.016。含金(砷)细粒高镁石英闪长岩的K-Ar年龄为42.54±0.94Ma和43.21±1.14Ma,其岩浆可能是由地球化学性质类似于哲古错辉长岩的底侵玄武质下地壳部分熔融形成的,此底侵玄武质岩浆源自轻度富集EMⅡ物质的大陆下岩石圈地幔,于晚侏罗世底侵到下地壳。距今65Ma前,印度板块与欧亚大陆碰撞,地壳逐渐加厚。约43Ma前,地壳加厚到40km以上,同时发生了构造事件,诱发玄武质下地壳熔融形成含金(砷)细粒高镁石英闪长岩岩浆,此岩浆与构造活动耦合上升到地壳浅部成岩成矿。细粒高镁石英闪长岩是对金成矿有利的岩石,并且赋存有斑岩型金(砷)矿(化)体,指示特提斯喜马拉雅东段可能存在斑岩型金矿带;同时,含金(砷)细粒高镁石英闪长岩的发现对特提斯喜马拉雅带构造-岩浆作用及地球动力学研究也有意义。 相似文献
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Arsenic derived from mining activity may contaminate water, soil and plant ecosystems resulting in human health and ecotoxicological risks. In this study, exposure assessment of arsenic (As) in soil, spoil, pondwater and plants collected from the areas contaminated by mine tailings and spoils in and around the La Parrilla mine, Caceres province, Spain, was carried out using AAS method. Water solubility, bioavailability and soil–plant transfer coefficients of As and phytoremediation potential of plants were determined. Arsenic concentrations varied from 148 to 2,540 mg/kg in soils of site 1 and from 610 to 1,285 mg/kg in site 2 exceeding the guideline limit for agricultural soil (50 mg/kg). Arsenic concentrations in pond waters varied from 8.8 to 101.4 μg/l. High concentrations of water-soluble As in the soils that ranged from 0.10 to 4.71 mg/kg in site 1 and from 0.46 to 4.75 mg/kg in site 2 exceeded the maximum permitted level of water-soluble As (0.04 mg/kg) in agricultural soils. Arsenic concentrations varied from 0.8 to 149.5 mg/kg dry wt in the plants of site 1 and from 2.0 to 10.0 mg/kg in the plants of site 2. Arsenic concentrations in plants increased in the approximate order: Retama sphaerocarpa < Pteridium aquilinum < Erica australis < Juncus effusus < Phalaris caerulescens < Spergula arvensis in site 1. The soil–plant transfer coefficients for As ranged from 0.001 to 0.21 in site 1 and from 0.004 to 0.016 in site 2. The bioconcentration factor based on water-soluble As of soil varied from 3.2 to 593.9 in the plants of site 1 whereas it varied from 2.1 to 20.7 in the plants of site 2. To our knowledge, this is the first study in Europe to report that the fern species P. aquilinum accumulates extremely low contents of As in its fronds despite high As levels in the soils. Therefore, the S. arvensis, P. caerulescens and J. effusus plant species grown in this area might be used to partly remove the bioavailable toxic As for the purpose of minimization of mining impacts until hypothetical hyperaccumulating and/or transgenic plants could be transplanted for the phytoremediation of As contaminated soils. 相似文献
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超声提取-氢化物发生-原子荧光光谱法测定水系沉积物中As(Ⅲ)和As(Ⅴ) 总被引:1,自引:1,他引:0
在50℃条件下,使用4.8 mol/L HCl超声提取水系沉积物中的As,氢化物发生-原子荧光光谱法测定As(Ⅲ)和总As的含量,用差减法计算As(Ⅴ)的含量。实验了柠檬酸、柠檬酸钠、草酸、草酸钠、酒石酸和酒石酸钠对As(Ⅴ)的掩蔽效果,通过控制合适的介质酸度选择性地测定As(Ⅲ)。结果表明,柠檬酸钠掩蔽As(Ⅴ)的效果最佳,且As(Ⅲ)有较高的灵敏度;超声提取30 min,柠檬酸钠浓度为6 g/L,测定酸度为0.24 mol/L时可获得最佳测定效果,降低了测定时As(Ⅴ)对As(Ⅲ)产生的信号干扰。方法检出限为0.41μg/L,相对标准偏差为1.33%(n=11),标准曲线线性范围为1.5~250μg/L。As(Ⅲ)和As(Ⅴ)的加标回收率分别为82.7%~95.3%和96.1%~107.6%。方法操作简便快速,准确度高,分析成本低,应用于水系沉积物中As(Ⅲ)和As(Ⅴ)的价态分析测定,获得了满意的结果,可满足大批量地质样品的分析要求。 相似文献
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Sb, As, Cu, and Zn toxicity and contamination have become a growing concern in recent years. Phytoremediation, a plant based and cost effective technology, may be an effective approach in the cleanup of water contaminated by these metals. In this study, the aquatic macrophyte Eleocharis acicularis was used in laboratory and field experiments to assess its capability to accumulate Sb, As, Cu, and Zn, and thereby investigate its potential application in phytoremediation. The results showed that E. acicularis adapted well to water contaminated by these metals. The removal rates of Sb, As, Cu, and Zn in the laboratory experiment were 3.04, 2.75, 0.417, and 1.49 μg/L/day, respectively. The highest concentrations of these metals accumulated in E. acicularis after 10 days of the laboratory experiment were 6.29, 6.44, 20.5, and 73.5 mg/kg dry weight, respectively. Only 8% of As, 12% of Sb, 87% of Cu and 93% of Zn removed from the water were used by E. acicularis. The highest concentrations of Sb, As, Cu, and Zn accumulated in E. acicularis after 10 wk of the field experiment were 76.0, 22.4, 33.9, and 266 mg/kg dry weight, respectively. The results indicate that E. acicularis has the ability to accumulate Sb, As, Cu, and Zn from contaminated water. 相似文献