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1.
魏正贵  尹明等 《生态学报》2001,21(6):900-906
ICP-MS法测定了江西赣南地区非稀土矿区和4处不同稀土矿区内,土壤-铁芒萁系统中15个稀土元素的含量,并对稀土元素在土壤剖面层及铁芒萁植物体内的分布、迁移特征进行了研究。结果表明,稀土元素总量在土壤剖面层的底土层含量最高,但表土层铈相对富集。稀土在铁芒萁植物体内的分布规律是叶、根>茎>叶柄。铁芒萁根中稀土元素的丰度与其母土表土层,尤其是母土表土层可溶态稀土元素的分布模式基本相似,稀土元素在铁芒萁体内的迁移过程中,发生了明显的分馏作用,茎、叶柄、叶中的重稀土相对贫乏。  相似文献   

2.
用感耦等离子体发射光谱法(ICP-AES)测定了江西赣南地区非稀土矿区和处不同稀土矿区内,土壤-铁芒萁系统中La、Ce、Pr、Nd、Sm、Gy、Db、Yb和Y的含量,并对其在土壤剖面层及铁芒萁植物体内的分布、迁移特征进行了研究.结果表明,土壤剖面层的底土层含量最高,但表土层铈相对富集.稀土元素总量(∑REE)在铁芒萁植物体内的分布规律是叶>根>茎>叶柄,单一稀土元素的分布规律各异,La、Ce、Pr、Nd的分布规律表现为:叶>根>茎>叶柄;Sm和Gd在不同采样点表现为叶>根>茎>叶柄或根>叶>茎>叶柄;Dy、Yb和Y均有3种不同的分布模式:叶>根>茎>叶柄、根>叶>茎>叶柄及根>茎>叶>叶柄.稀土元素在铁芒萁体内的迁移过程中,发生了明显的分馏作用,茎、叶柄、叶中的重稀土相对贫乏.  相似文献   

3.
用感耦等离子体发射光谱法(ICP-AES)测定了东西赣南地区非稀土矿区和4处不同稀土矿区内,土壤-铁芒萁系统中La、Ce、Pr、Nd、Sm、Gd、Dy、Yb和Y的含量,并对其在土壤剖面层及铁芒萁植物体内的分布、迁移特征进行了研究,结果表明,土训层的底土层含量最高,但表土层铈相对富集、稀土元素总量(∑REE)在铁芒萁植物体内的分布规律是叶>根>茎>叶柄,单一稀土的分布规律各异,La、Ce、Pr、Nd的分布规律表现为:叶>根>茎>叶柄;Sm和Gd在不同采样点表现为叶>根>茎>叶柄或根>叶>茎>叶柄;Dy、Yb和Y均有3种不同的分布模式:叶>根>茎>叶柄、根>叶>茎>叶柄及根>茎>叶>叶柄,稀土元素在铁芒萁体内的迁移过程中,发生了明显的分馏作用,茎、叶柄、叶中的重稀土相对贫乏。  相似文献   

4.
南方稀土采矿恢复地土壤稀土元素含量及植物吸收特征   总被引:3,自引:0,他引:3  
通过野外取样调查和室内ICP-MS测定,研究了福建省长汀县稀土矿治理地土壤和主要植物中稀土元素的含量、分布以及转移特征.结果表明:稀土矿治理地的土壤养分含量较低;土壤中稀土元素的含量为507.40~841.37 mg· kg-1,高于对照地土壤的含量.稀土矿治理地土壤中稀土元素主要为交换态,其含量占总量的61%~98%.稀土矿治理地土壤中稀土元素从原来偏单一的交换态转变为多种形态共存,其中有机态含量显著升高.植物根、茎、叶中稀土元素含量分别为40.27~986.01、5.14 ~ 206.58、6.81 ~ 2364.51mg·kg-1.稀土元素在植物各器官中含量水平除芒萁为叶>根>茎,其他植物均表现为根>叶>茎.根据不同植物吸收和积累稀土元素的差异,可将矿区治理地植物分为富集型和根部囤积型植物.芒萁属于富集型植物,桉树、高羊茅、宽叶雀稗、木荷和油茶属于根部囤积型植物.  相似文献   

5.
La、Ce、Nd、Tb、Dy 等稀土元素在铁芒萁( Dicranopterisdichotoma Underw) 体内的分布规律是叶> 根> 茎, 而Pr、Sm 、Eu、Gd、Ho 和Y等稀土元素在铁芒萁体内的分布规律是根> 叶> 茎。轻、中稀土元素容易被吸收和积累,并表现出选择性吸收。铁芒萁叶绿素中结合有较多的稀土元素,且主要是轻稀土元素,其中La 含量最高,占56 .08% ,其次是Ce,占19 .40% 。利用荧光X射线吸收精细结构(FXAFS)光谱表征出,在铁芒萁体内La 是与两个卟啉环配位的,推断叶绿素镧为双层结构  相似文献   

6.
在我国施用稀土时间最长的黑龙江省花园农场,研究比较了施用稀土12a和不施稀土的对照处理上小麦和土壤中的稀土元素的分布、累积及运移。结果表明,长 期叶面稀土未造成耕土壤和下部土层的稀土元素的累积,成熟期小麦植株各部的稀土元素含量顺序为根>叶>茎、壳;稀土元素主要累积在根部,其次是叶,茎和壳累积较少。喷施处理小麦根部的稀土元素累量高于对照,叶部也有此趋势,而茎,壳等部位差异不大。根、茎、叶、壳稀土元素  相似文献   

7.
研究了大冶钢绿山矿区海洲香薷(Elsholtziahaichowensis)及其群落中几种主要植物Cu、Mn、Zn、Cd、Pb的累积分布,植物与土壤元素、Cu矿的关系,并对海洲香薷的重金属耐受性、铜矿的指示作用作了初步探讨.结果显示海洲香薷植物中的元素表现为Cu>Mn>Zn>Pb>Cd.其中Cu、Mn、Pb元素含量表现为根>叶>茎,Zn、Cd表现为叶>根>茎.和其它植物相比,海洲香薷中的Cu、Mn、Cd含量均高于其它植物,是其它植物的1~10倍.海洲香薷与土壤元素关系中,Cu的相关性最显著,其次为Pb.海洲香薷集中分布于矿区内含Cu较高的土壤上(1645~8950ug/g),其分布与Cu密切相关.  相似文献   

8.
茶园土壤类型对铁观音茶叶稀土元素分布和组成的影响   总被引:1,自引:0,他引:1  
为探明铁观音茶的质量安全状况,追溯隐患来源,对福建安溪县不同土壤茶园的铁观音茶叶进行稀土元素的分布、组成、迁移和富集能力进行研究。结果表明,安溪县红壤、黄红壤、黄壤茶园稀土组成均以镧、铈、钕、钇为主,但具体组成特征各异。3种类型土壤茶园铁观音茶叶片、叶柄稀土元素组成均以钇、镧、铈、钕4种元素为主,且含量均以第3叶第2叶第1叶叶柄。同种土壤类型茶园铁观音茶树不同部位叶片的稀土元素组成特征类似,但叶与叶柄对稀土元素的吸收能力不同。土壤类型对茶叶稀土元素的累积有显著影响,黄红壤茶园的茶叶稀土元素含量要显著低于红壤、黄壤茶园的(P0.05)。土壤与茶叶中稀土元素组成的相关系数为0.886~0.985,P 0.001,表明二者稀土元素组成密切相关。因此,铁观音茶叶中稀土元素累积、分布与茶园土壤类型有显著相关性。  相似文献   

9.
在我国施用稀土时间最长的黑龙江省花园农场,研究比较了施用稀土12 a和不施稀土的对照处理上小麦和土壤中的稀土元素的分布、累积及运移.结果表明,长期叶面喷施稀土并未造成耕层土壤和下部土层的稀土元素的累积.成熟期小麦植株各部位的稀土元素含量顺序为根>叶>茎、壳;稀土元素主要累积在根部,其次是叶,茎和壳累积较少.喷施处理小麦根部的稀土元素累积量高于对照,叶部也有此趋势,而茎、壳等部位差异不大.根、茎、叶、壳稀土元素分布模式与土壤中相似,与施用的常乐稀土差别较大;长期喷施稀土未曾造成籽粒中稀土元素的明显累积.  相似文献   

10.
俞斌  夏会龙 《应用生态学报》2013,24(6):1615-1620
采用盆栽试验,研究了茶籽粕和EDTA对土壤中重金属镍和锌形态变化和植物有效性的影响.结果表明:随着茶籽粕施用量的增加,甘蔗根、茎、叶的生物量逐渐增加,而EDTA处理甘蔗茎、叶的生物量与对照无显著差异.茶籽粕和EDTA的添加提高了土壤中酸溶态镍和锌含量,促进甘蔗对镍和锌的吸收及向地上部位转运,并且随着茶籽粕施用量的增加,其促进效果逐渐增强.与EDTA相比,茶籽粕对提高甘蔗体内镍和锌积累量效果明显,使甘蔗从土壤中迁移出更多的镍和锌.甘蔗茎、叶中镍和锌含量与茶籽粕的用量呈极显著正相关,而根中镍和锌含量与茶籽粕用量呈极显著负相关.  相似文献   

11.
Abdehpour  Zahra  Ehsanzadeh  Parviz 《Plant and Soil》2019,437(1-2):427-437
Plant and Soil - Dicranopteris linearis is a fern that accumulates unusually high concentrations (up to 0.3% dry weight) of rare earth elements (REEs) in China. Previously, we reported that D....  相似文献   

12.
阜新市农田土壤重金属含量及其分布特征   总被引:3,自引:0,他引:3  
通过对辽宁省阜新市城郊区县180处农田土壤的取样调查分析,初步了解了农田土壤重金属As、Cu、Zn、Ni的含量特征及其空间分布,并探讨了当地矿业开采活动对农田土壤重金属积累及空间分布的影响.结果表明,研究区域内农田土壤Cu、Zn和Ni的几何平均含量均高于背景值,且这3种重金属存在普遍累积的现象;不同种植类型土壤中,菜地土壤Cu、Zn、As含量显著高于粮田,且重金属积累更为明显;4种重金属的空间分布均呈城区高于郊县的趋势;重金属含量较高的区域与矿山开采区域基本重叠.研究区域内采矿活动是农田重金属的重要来源,同时畜禽养殖业所产生的畜禽粪便可能对农田土壤中Cu、Zn和As的增加有一定作用.当地农牧业生产和布局应适当考虑土壤污染的风险.  相似文献   

13.
The widespread use of rare earth elements (REEs) has resulted in problems for soil and human health. Phytolacca americana L. is a herbaceous plant widely distributed in Dingnan county of Jiangxi province, China, which is a REE mining region (ion absorption rare earth mine) and the soil has high levels of REEs. An investigation of REE content of P. americana growing naturally in Dingnan county was conducted. REE concentrations in the roots, stems, and leaves of P. americana and in their rhizospheric soils were determined. Results showed that plant REEs concentrations varied among the sampling sites and can reach 1040 mg/kg in the leaves. Plant REEs concentrations decreased in the order of leaf > root > stem and all tissues were characterized by a light REE enrichment and a heavy REE depletion. However, P. americana exhibited preferential accumulation of light REEs during the absorption process (from soil to root) and preferential accumulation of heavy REEs during the translocation process (from stem to leaf). The ability of P. americana to accumulate high REEs in the shoot makes it a potential candidate for understanding the absorption mechanisms of REEs and for the phytoremediation of REEs contaminated soil.  相似文献   

14.
Ong  Bee-Lian  Chan  Sau-Siong  Turner  I.M. 《Photosynthetica》1998,34(2):317-320
Photosynthetic characteristics, specific leaf mass, chlorophyll and total leaf nitrogen concentrations of four herbaceous plants (Dicranopteris linearis, Hanguana malayana, Pentaphragma ellipticum, Tacca integrifolia) from nutrient-poor tropical forests showed that all these plants were well-adapted to their natural growth environments. No photoinhibition was observed even in the understorey plants.  相似文献   

15.
Rare earth elements (REEs) are widely used in industry and the entry of REEs into the pedosphere is assumed. Data about REEs in soils are scarce since only a few studies discuss their ecologically relevant behavior. Hence, we investigated total contents (aqua regia digestion) and potentially bioavailable contents (EDTA extraction) of REEs in soils from the Nidda catchment in Hesse (Central Germany). The study site covers a 1,600 km² sized area and 232 soil samples from 63 soil profiles were examined. The total REE content varied considerably, ranging from 544 mg kg?1 to 41 mg kg?1 (mean 201.1 mg kg?1) with a high proportion of light REEs. Highest REE contents were found in the soilscape VB, followed by LVB, WNE, T, WSW and BF with the smallest concentrations. With respect to the parent material the contents decreased in the following order: basalt > clay slate > loess > sandstone. On average 15.9% of the total REEs belong to the potentially bioavailable fraction. They range greatly by a factor of 100, between 1.3 and 171.3 mg kg?1 (average 33.5 mg kg?1). Remarkably, Yttrium has a maximum available proportion of 75%. In contrast, Ce showed the highest total contents with the smallest potentially bioavailable proportion of all elements. Regression analyses established relation between soil properties and the potential bioavailability of REEs. Around 53% (range from 29.9 to 76.8%) of the REE’s potential bioavailability variations could be explained by the chosen variables (pH, clay and Corg contents and the total element concentrations). Occurrence patterns and concentrations of REEs lie within the range of the results found in the available literature. Bioavailability is linked to soil properties and varies greatly according to the individual element. In comparison with the chosen soil properties the pH value shows the least impact on bioavailability.  相似文献   

16.
金属矿区芒草种群对重金属的积累及其与土壤特性的关系   总被引:9,自引:0,他引:9  
通过分析大型综合金属矿区中经历不同污染强度与污染时间胁迫的芒草(Miscanthus sinensis)种群对4种主要重金属的积累状况,初步揭示芒草对这些重金属的积累特性与土壤重金属含量的关系。结果表明,1芒草根茎叶对4种重金属的的积累顺序为:根〉叶〉茎;2芒草对Cd、Pb的积累量与土壤中这两种重金属含量之间存在显著(P〈0.05)正相关关系;对Cu、Zn的积累量与土壤含量之间无显著相关,主要是因为土壤最高Cu与Zn含量已超过芒草对这两种元素积累所需的最大量,成为对芒草构成胁迫的主要因子。在该矿区的酸性条件下,芒草对Pb、Zn、Cu3种重金属的吸收率随pH值升高而升高,pH接近的样地,芒草的吸收率主要受土壤重金属含量的影响。结合各种群对四种重金属的积累状况判断,强度胁迫下的种群可能已发生耐性分化,从而产生较其它种群更强的耐重金属特性。总体上芒草是一种多重金属耐性植物,对这四种重金属的耐性顺序是:Cd〈Cu〈Zn-Pb。  相似文献   

17.
Fu  FengFu  Akagi  Tasuku  Yabuki  Sadayo  Iwaki  Masaya 《Plant and Soil》2001,235(1):53-64
Rare earth elements (REEs) in five species of soil-grown plants (Taxodium japonicum, Populus sieboldii, Sasa nipponica, Thea sinensis and Vicia villosa) and in the soil on which each plant grew were determined with an inductively coupled plasma mass spectrometer (ICP-MS) in order to observe the variation in the distribution of REEs and to elucidate their source in soil-grown plants. The plant samples were divided into root (secondary root and main root), trunk (stem) and leaf; the soils into water soluble (soilsoluble fraction), HCl and HNO3 soluble (soilnon-silicate fraction) and HF soluble (soilsilicate fraction). The REE abundances of samples were compared using REE patterns where the abundances were normalized to those of a chondrite and plotted on a logarithmic scale against the atomic number. All the plants showed similar REE patterns independent of species and location, and a W-shape variation (W-type tetrad effect) and abundance depletion of cerium (negative Ce anomaly) were found in each REE patterns of plants, more conspicuous tetrad effect being observed in HREE (heavier rare earth elements) region than in LREE (lighter rare earth elements) region. The overall variation of REE patterns of each secondary root was not similar to that of soilsoluble fraction, but similar to that of soilsilicate fraction except for the tetrad effect and Ce anomaly. The REE patterns can be interpreted by the idea that plants of different species take in REEs and Si from different parts in the soil. The results of this study seem to imply that Sasa nipponica and Vicia villosa take in free REEs and Si rather directly from silicate in the soil, and that a majority of REEs and Si in Taxodium japonicum and Thea sinensis are originated from the soluble fraction in the soil.  相似文献   

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